aloke mookherjea paper sponge iron project
TRANSCRIPT
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PRELIMINARY POSITION PAPER
ON
PROJECT PROPOSAL
FOR
REPLACEMENT OF INJECTION COAL BY
PARTIALLY STEAM REFORMED
COAL - BED METHANE (CBM)
IN
CONVENTIONAL COAL BASEDSPONGE IRON PLANT IN A
DIRECT REDUCTION PROCESS
Aloke MookherjeaChairman
Flakt (India) Limited[Email : [email protected]]
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Introduction
Originally, when direct reduction of iron or DRI plants were envisaged, the idea was to replace
coke whose availability and cost became highly uncertain and prohibitive. The original process
of DRI replacing coke and using coal was hailed as a precursor of a new regime of making iron
and steel.
Then started the problem always associated with the use of coal as fuel. Coal, while being a
comparatively cheaper fuel and (which is a common knowledge today) has a no. of reasons for
being used as a fuel, particularly in developing countries like China and India, also has inherent
problems of creating environmental pollution. This happens because of air/gas pollution, solid
waste, causing water pollution and very high emission of greenhouse gases like carbon dioxide.
While use of any hydrocarbon like methane etc. will not remove the generation of carbon
dioxide totally, it certainly reduces the emission and takes away the problem of other kind of
environmental degradation. This degradation is very prominent now all over the country
wherever there is a concentration of sponge iron plant, like Durgapur and Birbhum area of West
Bengal.
It has been proposed to establish theoretically, as well as practically that Coal Bed Methane(CBM), abundantly available in these areas or near about in West Bengal, could replace the use
of injection coal.
The basic improvements expected from such a process modification would be a much higher
reducing efficiency for the iron ore because of higher hydrogen density of methane compared to
that of coal and of course much less generation of all kinds of waste which is normal with the
use of coal.
Metallurgy
Direct reduction of iron ore, an alternative to blast furnace technology of producing iron from
ore, has become very popular because of reasons stated above. In this process, the ore isconverted into metallized pellets, the so called sponge iron, by removing the oxygen from the
iron to leave metallic iron. The amount of metallic iron produced from a given quantity of ore is
termed as the degree of metallization and is defined by the ratio of the amount of the metallic
iron produced to that of total iron in the ore.
The iron left after the removal of oxygen has a honeycomb like construction and hence the name
sponge iron. A considerably high degree of purity of ore is required for sponge iron because the
gangue is not removed at the iron making stage but later in the steel making process. Both
pelletised concentrate and screened natural lump ore of similar purity can be utilized. A typical
layout of the sponge iron is given in Diagram 1 where the heart of the process is the Rotary
Kiln. Ore (Fe2O3) with coal and a small amount of dolomite (flux) is fed to the Rotary kiln
which also has an arrangement of submerged air injection. Obviously there is a lot of material
handling involved in different stages because of use of the ore and coal. The chemistry of the
iron formation is given in Diagram 2. Haematite or iron ore and the non-coking coal are the
major raw materials. The significance of this process is that coal plays a dual role by acting as a
reducing agent as well as the fuel for raising the requisite temperature inside the kiln to more
than 1000C. Another point in this process is that the reduction occurs in solid state. Controlled
combustion as well as the conversion of carbon monoxide to remove oxygen from the iron ore
are the crucial factors in this process.
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Diagram 1
Diagram 2
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Reactions
Using haematite or Fe2O3 as the ore, the carbon monoxide and hydrogen which are both
reducing gases act on the ore and reduces it to metallic iron at a temperature above 800 deg. C.
In the pre-heat zones, the temp is around 850-1000 deg C while the reduction zone temp is
around 1000/1050 degC. As normal in all kiln type of operation, the moisture is driven off first
and after that thermal decomposition of coal and subsequent generation of reducing gases like
HCs and H2 take place. Also, as normal in a rotating kiln, the major heat transfer to the chargetakes place through the mechanism of radiation. Gases are burnt above the bedassisted by
controlled air injection, also helping in better fuel consumptionand more heat is transferred
through mixing and constant change in the charge layer.
The stages are :
Fe2O3+ CO= 2FeO + CO2 (Ferric to Ferrous Oxide)
FeO+ CO= Fe+CO2 (reduction in metallizing zone)
CO2+C (presence of excess solid fuel) = 2CO
The beds are not excessively heated up as the 3rd
reaction above is endothermic, thus no melting
or stickiness.
Methane & Steam Reforming of Methane
Thermodynamically methane has a great reducing capability and can be activated to produce
synthetic gases over heated metal oxide as an oxygen donor. Metal oxide reduction and methane
activation, two concurrent thermo-chemical process, can be combined as an efficient and energy
saving process. This new reduction process combines energy efficiency and much lower degree
of GHG emission compared to the conventional process using coal.
Partial steam reforming of methane with sub-stoichiometric amount of H2O ensures that there is
hardly any water gas shift reaction taking place and very little or no CO is lost as carbon dioxide
before the main reaction zone of direct reduction.
The steam reforming of methane consists of 3 reversible reactions as given below where 1 and 3
are strongly endothermic reactions while the water gas shift reaction in equation 2 is moderately
exothermic.
CH4 + H2O CO + 3H2 deltaH deg 298 = +206 kJ/mol (1)
CO + H2O CO2 + H2 deltaH deg 298 = - 41 kJ/mol (2)
CH4 + 2H2O CO2 + 4H2 deltaH deg 298 = +165 kJ/mol (3)
One must note that CO2 is not only produced via the shift reaction as in 2 above but also directly
via the steam reforming reaction in equation 3 above. It only emphasizes the fact that 1 and 2
are not the only reactions occurring during the reforming processes.
Because of its endothermic character, reforming is favoured by high temperature. Also because
of volume expansion it is favoured by low pressure. On the other hand, exothermic shift reaction
is favoured by low temp but unaffected by pressure change. Increasing the amount of steam will
no doubt enhance the methane conversion but would also require additional amount of energy to
produce the steam. In practice, steam to carbon ratio (S/C) of around 3 are applied.
The steam reforming process is divided into 2 sections, a section of high temperature and
pressure, of around 800 to 1000 deg. C and 30 to 40 bar pressure, in which the reforming and the
shift reaction occur. This is followed by additional 2 step shift section at lower temperature
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(typically of the order of 200-400 deg. C) in order to maximize the CO conversion via reaction
no. 2 shown above. In such a process, CO concentration can be as low as 0.1%.
The steam reforming further decreases the demand of elemental oxygen for converted carbon to
CO, thus requiring less volume of air. This also helps in reducing the amount of diluents in the
reaction zone. It is clear that a very important feature of steam reforming is the generation of
elemental hydrogen which is extracted from both methane as well as water vapour. This
generates hydrogen which is theoretically 3 moles per mole of methane reformed which in turn
will act as an even more efficient reductant as compared to CO. In this process the carbondemand also decreases.
OBJECTIVE
It has been proposed that coal based methane as a fuel and a reductant can be very helpful for
sponge iron plants in Eastern India. CBM has the same benefits as normal natural gas and can
be substituted for natural gas as long as it has a low sulphur content and high methane content of
around 94% plus. This should normally pose no problem based on the analysis of the CBM
available. This process also is expected to comply with very stringent environmental
compliance.
A techno-economic feasibility study is being planned for making the above possible. It isproposed that initially certain laboratory studies would be needed to find out the actual high
reducing ability of steam reformed methane. It has been given to understand that NML at
Jamshedpur can carry out this study and come out with the answer. After this study the pilot
plant will be required to be set up at one of the sites. Based on the current operational
parameters of variable load vis--vis amount of coal injected as well as its properties such as
chemical analysis, calorific value etc. trial and error method has to be adopted for gradual
replacement of coal by steam reformed CBM to arrive at the optimum condition. Theoretical
calculations beforehand would no doubt help but actual experimentation must be carried out at
site in a pilot plant to achieve the optimum conditions. Also, the normal current practice of coal
injection at the discharge end has to be looked into. Today, this is done purportedly for
preventing carbon starvation as also for maintaining the temperature profile in the kiln.
Even if the pilot study is done for part load and/or a small sized kiln, low pressure steam would
be required at site as well as a small reformer using heated nickel plate or other material.
Extensive trials and tabulations of data would be necessary.
The next step would be analysis and interpretation of data for subsequent use in a scaled up plant
with continuous supply of steam and CBM. It is also understood that supply of methane will not
be a problem since even for todays production of CBM, a lot of gas is being flared up. The
pilot plant study could be made with piped supply if possible but even otherwise it can be
supplied from a tanker. For final implementation of course, continuous piped supply would be
necessary.
The first step in the project will be the initial formulation. Next will be the laboratory studies
after which calculations and design of the experiment could be taken up. The pilot plant
including the additional equipment required could be set up after this. Actual experiments
including collection of site data etc. would follow. The last step would be the interpretation of
the data and analysis of the same after which the work to scale up model can be started.
The time period for all these steps will depend upon the resource provided and time spent. A
rough estimate could be around 32 weeks after work starts in right earnest up to the pilot plant
stage but this can vary widely depending upon the working conditions.