[0001] This invention relates to the suppression of toxic byproducts which are generated
during sintering of iron ore. In particular, the invention concerns a method of and
apparatus for suppressing the synthesis of chloro-organic pollutants, especially polychlorinated
dioxins and furins (hereinafter referred to as PCDD/Fs), and the release of acidic
gases during sintering.
[0002] The conversion of iron ore into for example iron rich agglomerates, for subsequent
reduction in blast furnaces is a process known as sintering. The sinter process comprises
heating a layer of iron ore until partial melting occurs to cause individual iron
particles to become fused together. The heat necessary to achieve this is provided
by forced combustion of fine coke (known as coke breeze) which is mixed
inter alia with the iron ore to be reduced and fluxes prior to delivery to a sinter plant. The
process is continuous; a travelling grate transports the sinter mix as a bed to an
ignition hood which ignites the coke in the upper surface of the sinter bed. Thereafter,
the combustion of the coke lower down in the mix is maintained by air flowing through
the bed. The air flow may be generated by a suction fan. Typically, the travelling
grate carries the sinter mix over a series of "wind boxes" which draw air through
the sinter mix.
[0003] In a conventional sinter strand, the waste gases pass from wind boxes through "wind
legs" which link to a "wind main". These gases contain noxious emissions including
inter alia PCDD/Fs, oxides of nitrogen and other acidic compounds such as hydrogen chloride
and sulphur dioxide. Therefore, the waste gas is typically treated to clean the gas
before being exhausted to the atmosphere.
[0004] PCDD/Fs present two of the most potentially harmful combustion by-products of the
sinter process. PCDD/Fs are a family of chlorinated organic compounds having a general
formula (A) and (B) respectively:

[0005] The degree of toxicity varies and depends on the number and position of chloride
substitutions on the aromatic carbon ring.
[0006] There is evidence to suggest that PCDD/F precursors are formed from the pyrolysis
and chlorination of the organic material that represents the more primary combustion
products such as hydrogen chloride, carbon monoxide, water, hydrogen, ethylene and
acetylene. PCDD/Fs are thus synthesised
de novo as a result of thermal reactions between precursor compounds. For example, the precursor
pentachlorophenol (C) can interact to produce the dioxin octachlorodioxin (D). After
formation, some of the PCDD/Fs may recombine downstream to produce a different set
of compounds which may have higher or lower toxicity. Some of the non-toxic isomers
may be converted to toxic isomers and vice versa.
[0007] It is also claimed that the 'fingerprint' of toxic isomers is specific to their formation
mechanism; for example in combustion processes, furans are synthesised to a greater
extent than dioxins and the pentachlorinated furan is the major contributor to total
toxicity.
[0008] The increasing awareness of the long term deleterious effects on the environment
by the release of such toxic compounds into the atmosphere, has generated a need to
produce a relatively cheap and effective mechanism of decreasing the chloro-organic
and acidic compounds released as gaseous by-products of combustible processes.
[0009] In the past, much effort has been directed towards reducing the toxic organic gases
released in stack emissions from incineration of municipal waste materials. The most
frequently applied control technology involves the use of a spray dryer absorber followed
by a particulate matter control device, most commonly a fabric or activated carbon
filter. This technology controls the emission of acidic gases such as hydrogen chloride
by providing a neutralising reaction with calcium carbonate (lime). The resulting
solid materials (e.g.CaCl
2) are captured downstream of the lime injection site. PCDD/F gases are assumed to
be captured by surface absorption by the filter deposit. Although this method reduces
gaseous toxic emissions from incinerator plants to a limited extent, it is capital
intensive and procedurally complex. In addition, it significantly increases the mass
of solid waste to be disposed of and introduces the problem of toxic chloro-organic
solid waste disposal.
[0010] Another method used in municipal waste disposal is exemplified in EP-A-371945. This
document discloses a method for extracting dioxins from a gas which comprises contacting
the gas with a liquid aerosol over a predetermined period of time. The particles present
in the aerosol are electrically charged and subsequently separated from the gas with
the aid of a wet electrostatic precipitator or electric field.
[0011] Ammonia gas or ammonia releasing compounds such as alkanolamines, have demonstrated
a potential to control simultaneously emissions of several pollutants of concern,
such as dioxins, hydrogen chloride, sulphur dioxide and oxides of nitrogen.
[0012] The present inventors have disclosed in EP-A-0 875 587 an efficient and cost effective
method of reducing toxic emissions, more especially PCDD/F formation, from a sinter
strand, whilst keeping the quantity of ammonia gas released into the atmosphere at
low levels and without the need to introduce complex modifications to existing strand
equipment.
[0013] Their method comprised the sequential steps of producing a sinter feedstock by substantially
homogeneously mixing
inter alia iron ore with 0.01 to 0.09% by weight of a solid compound which releases ammonia
on thermal decomposition, depositing said feedstock onto moving grate and combusting
the same to produce sintered products rich in iron.
[0014] The present inventors have now discovered an alternative method of reducing toxic
emissions
with or without the addition of exogenous chemicals to the sinter strand.
[0015] Dioxins are known to be formed in the approximate temperature range 200 to 400°C.
Dioxin formation has been reduced in other industries by ensuring that waste gases
which may produce dioxins are cooled to below 250°C as soon as possible to avoid prolonged
reaction times in this critical temperature range. However, in a sinter strand the
situation is more complex; the gas passes through a packed bed of sinter mix and the
gas temperature at the bottom of the sinter strand as it enters each wind box will
be different depending on the position of the wind box along the strand. Typically,
for the first 70% or so wind boxes, the exit temperature is relatively stable at approximately
100°C. This rapidly rises towards the end of the strand, peaks at up to 400°C and
then drops slightly at the end of the strand.
[0016] It has been found that a good correlation exists between the gas temperature at the
sampling point and the dioxin level measured in the gas. Figure 1 illustrates the
correlation between the temperature of the waste gases and the windleg number along
the sinter strand. Figure 2 illustrates the correlation between the PCDD/F formation
in the waste gases and the wind box number along the sinter strand.
[0017] Accordingly, in one aspect the invention provides a method of sintering iron ore
in a sinter strand comprising providing a sinter feedstock and depositing said feedstock
onto a travelling grate, igniting said feedstock using a sinter strand burner(s),
and combusting said feedstock by drawing air through the feedstock with a plurality
of wind boxes situated along the length of the strand, to produce sintered products
rich in iron and waste gases,
characterised in that waste gases from only those wind boxes whose temperature
exceeds a predetermined level are recycled to provide combustion feed air for the
feedstock or air for the sinter strand ignition burner(s), in order to substantially
reduce or eliminate the production and/or emission of dioxins.
[0018] It has been found that recycling the waste gases in this way consumes the dioxins
at the flame front as the dioxins pass through the sinter mix or at the burner.
[0019] Preferably, waste gases of a temperature greater than 200°C are recycled. Typically,
waste gases of a temperature greater than 250°C are recycled. As figure 2 shows, it
has been found that significant dioxin formation only occurs in the wind boxes wherein
the temperature of the gases exceeds approximately 200°C.
[0020] In one embodiment of the invention, the waste gases are recycled from the final 25%
of the wind boxes, preferably the final 20% of the wind boxes. Accordingly, the waste
gases may only be recycled from a wind box if the temperature of the waste gases present
within that wind box is greater than 200°C. Therefore, the advantage of the invention
in suit is that the toxicity of waste gases produced during sintering can be minimalised
by recycling only a
fraction of the total waste gas.
[0021] In one embodiment, the waste gases which have a temperature of greater than about
200°C may be rapidly cooled to below about 200°C to substantially reduce or eliminate
the production of dioxins.
[0022] In another aspect, the invention provides a method of sintering iron ore in a sinter
strand comprising providing a sinter feedstock and depositing said feedstock onto
a travelling grate, igniting said feedstock using a sinter strand burner(s), and combusting
said feedstock by drawing air through the feedstock with a plurality of wind boxes
situated along the length of the strand, to produce sintered products rich in iron
and waste gases,
characterised in that waste gases from the sinter strand which have a temperature
of greater than about 200°C are rapidly cooled to below about 200°C substantially
to reduce or eliminate the production of dioxins.
[0023] The invention may involve the cooling of the waste gases in one or more of the wind
boxes. In one embodiment, the temperature may be reduced by injecting a liquid or
a gas (e.g. gaseous ammonia) into the waste gases in the or each wind box, and/or
into the waste gases in their passage subsequent to the or each wind box. The liquid
may be water for example, the water may be added in the form of steam. Preferably,
the liquid comprises ammonia which may further reduce the level of dioxins in the
gas. The rate at which the liquid may be introduced may be determined by the rate
at which air is drawn into the wind boxes.
[0024] Alternatively or in addition, the external surface of the or each wind box and/or
the external surface of any conduit leading from the or each wind box may be cooled
by a supply of fluid, either liquid or gas, e.g. water, for example, in the form of
steam.
[0025] Alternatively or in addition, the travelling grate of the sinter strand may be cooled,
for example, with water, e.g. steam.
[0026] In another embodiment, a heat exchanger may be used to lower the temperature of the
waste gases.
[0027] The sinter feedstock may include 0.01 to 0.09% by weight of a solid compound which
releases ammonia on thermal decomposition. The ammonia compound may be substantially
homogeneously mixed with iron ore in the sinter feedstock.
[0028] In yet another aspect, the invention provides a sinter strand which includes means
for recycling waste gases from those wind boxes in the strand whose temperature exceeds
a predetermined level, to provide combustion feed air for sinter feedstock for subsequent
sintering, or air for a sinter strand ignition burner(s).
[0029] The sinter strand may further comprise means to cool waste gases which have a temperature
of greater than about 200°C to below about 200°C to substantially reduce or eliminate
the production of dioxins.
[0030] In still a further aspect, the invention provides a sinter strand which includes
means to cool waste gases from the sinter strand which have a temperature of greater
than about 200°C to below about 200°C to substantially reduce or eliminate the production
of dioxins.
[0031] The invention will now be described by way of example only, with reference to the
accompanying diagrammatic drawings in which:-
Figure 1 illustrates the correlation between the temperature of the waste gases and
the windleg number along the sinter strand as described in the text above;
Figure 2 illustrates the correlation between the PCDD/F formation in the waste gases
and the wind box number along the sinter strand as described in the text above; and,
Figure 3 illustrates a conventional sinter strand.
[0032] Referring now to Figure 3, the strand comprises a travelling grate 1, onto which
pre-mixed constituents of a sinter bed are deposited via a hopper 2. Mixing of these
constituents is effected in a blender 3. The mixed constituents include iron ore and
iron ore fines, burnt lime, coke breeze and optionally measured quantities of ammonia
releasing compounds in solid, e.g. pellet form.
[0033] The deposited sinter bed feedstock passes below an ignition hood 4, which ignites
the coke breeze, combustion being enhanced and continued by the flow of large quantities
of air, drawn through the bed by a series of wind boxes (not shown) along the stack.
Sintered ore leaves the bed at the end of the grate remote from the hopper 2 and passes
through a series of treatment stages. Waste gases of combustion leave the furnace
through more stacks 5.
[0034] The illustrated strand is typical of many conventional strands, the essential difference
being that the waste gases which contain levels of toxicity exceeding desired limits
are specifically recycled or that the waste gases of a temperature suitable for the
formation of toxic dioxins are rapidly cooled.
[0035] It will be appreciated that the foregoing is merely exemplary of methods and apparatus
in accordance with the invention and that various modifications can readily be made
thereto without departing from the scope of the invention.
1. A method of sintering iron ore in a sinter strand comprising providing a sinter feedstock
and depositing said feedstock onto a travelling grate, igniting said feedstock using
a sinter strand burner(s), and combusting said feedstock by drawing air through the
feedstock with a plurality of wind boxes situated along the length of the strand,
to produce sintered products rich in iron and waste gases,
characterised in that waste gases from those wind boxes whose temperature exceeds
a predetermined level are recycled to either provide combustion feed air for the feedstock
or air for the sinter strand ignition burner(s) in order to substantially reduce or
eliminate the production of dioxins.
2. A method as claimed in claim 1 wherein waste gases of a temperature greater than 200°C
are recycled.
3. A method as claimed in claim 1 or claim 2 wherein waste gases of a temperature greater
than 250°C are recycled.
4. A method as claimed in any one of the preceding claims wherein the waste gases are
recycled from the final 25% of the wind boxes.
5. A method as claimed in claim 4 wherein the waste gases are recycled from the final
20% of the wind boxes.
6. A method as claimed in any one of the preceding claims wherein the waste gases are
recycled from a wind box where the temperature of the waste gases (present within
that wind box) is greater than 200°C.
7. A method as claimed in any one of the preceding claims wherein the waste gases which
have a temperature of greater than about 200°C are cooled to below about 200°C to
substantially reduce or eliminate the production of dioxins.
8. A method of sintering iron ore in a sinter strand comprising providing a sinter feedstock
and depositing said feedstock onto a travelling grate, igniting said feedstock using
a sinter strand burner(s), and combusting said feedstock by drawing air through the
feedstock with a plurality of wind boxes situated along the length of the strand,
to produce sintered products rich in iron and waste gases,
characterised in that waste gases from the sinter strand which have a temperature
of greater than about 200°C are rapidly cooled to below about 200°C substantially
to reduce or eliminate the production of dioxins.
9. A method as claimed in claim 7 or claim 8 wherein the temperature of the waste gases
is reduced in a wind box.
10. A method as claimed in claim 9 wherein the temperature of the waste gases is reduced
by injecting a liquid or a gas (e.g. gaseous ammonia or steam) into a wind box.
11. A method as claimed in any one of claims 7 to 10 wherein the temperature of the waste
gases is reduced by adding liquid or gas (e.g. gaseous ammonia or steam) to the waste
gases after they leave the or each wind box.
12. A method as claimed in any one of claims 7 to 11 wherein the external surface of a
wind box and/or the external surface of any conduit leading from a wind box is cooled
by a supply of fluid.
13. A method as claimed in any one of the preceding claims wherein the sinter feedstock
includes 0.01 to 0.09% by weight of a solid compound which releases ammonia on thermal
decomposition.
14. A method as claimed in claim 13 wherein the ammonia compound is substantially homogeneously
mixed with iron ore in the sinter feedstock.
15. A sinter strand which includes means for recycling waste gases from only a selection
of wind boxes in a sinter strand whose temperature exceeds a predetermined level,
to provide combustion feed air for sinter feedstock for subsequent sintering, or air
for a sinter strand ignition burner(s), in order to substantially reduce or eliminate
the production of dioxins.