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Alumina Assignment

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Alumina Assignment
Joseph Griggs – S3436440
Q2.
a)
The presence of silicates in the Alumina refining process has two major disadvantages for the process
overall. If there is no attempt to remove the silicates, or they are improperly removed, the entire
process can come to a standstill while the scale formed on piping is treated. Not only does this slow
down the process, causing delays and a decrease in productivity for the plant, but money must also be
spent on removing the scale. There are two main ways to prevent scale build up: limit the ability for the
scale to form on the pipe surface, or remove the silicates early in the process to prevent them from
affecting the later stages. Silicates are removed by reacting the active silicate compounds with alkaline
solutions containing Cano (lime). This is done at a relatively high temperature (100°C) and takes 8~9
hours. During this process, aluminium in the form of Al2O3 and NaOH, a reactant used in the next
processing steps, is consumed.
The alternative is the prevent scale forming by adding chemicals which inhibits the scale formation. One
example of a scale inhibitor is Sodalite, which prevents scale by adhering to the surface of
aluminosilicate crystals which attach to the surface of piping. Once attached, the sodalite prevents
further crystal growth, preventing any further build up. This method of prevention involves the
introduction of a new chemical into the process costs, and any unreacted sodalite is a concern for later
stages in the process.
The Bayer process creates large amounts of ‘red mud’, a solution of iron and titanium oxides (giving it
the red colour) in sodium hydroxide. Much of this waste is simply stockpiled, as there are very few viable
uses for the by-product. The red mud can be stored in various ways depending on the concentration. For
low concentrations of 25-30% w/w mud lakes are used to stockpile the red mud, as the solution is
mostly liquid. This storage uses a large amount of land and so destroys local environment. Higher
concentrations (> 30% w/w) are usually stored as dry solids and take up much less space, but still
require some land use for storage, especially at lower percentages.
The two significant methods for dealing with red mud are carbonation and seawater neutralization.
Carbonation reduces the alkalinity of the red mud by forcing carbon dioxide through the red mud. This
reacts with the sodium hydroxide, reducing the pH from 13.5 down to 10.5 (as pH is a log scale this is
1000x reduction in alkalinity), reducing the potential harm the red mud can cause. The other process,
which can be quite expensive to due high energy and infrastructure required, is seawater neutralization.
Seawater is mixed with the red mud, allowing for naturally occurring calcium and magnesium ions to
react with the sodium hydroxide, reducing the pH. The reduction in pH is proportional to the amount of
seawater used to treat the red mud, but with enough seawater the red mud can be completely
neutralized, which is potentially viable for refineries near the coast.
b)
An alternative to liquor burning to remove organics midway through the Bayer process, is thermal pretreatment. This method submits the bauxite to thermal pre-treatment, producing a low temperature
digestible feed, with low concentrations of organics (Hollitt, Kisler, & Raahauge, 2002). To achieve
carbon removal, without loss of aluminium that is to be extracted, the bauxite must be stripped of any
water content. Thermal decomposition can also break down a portion of Boehmite in the bauxite into
more readily digestible alternatives, making this alternative pathway especially good for areas which
have high concentrations of Boehmite.
To process the bauxite, initially partial thermal dehydration occurs, which extracts carbon from the
bauxite and eliminates it (Hollitt, Kisler, & Raahauge, 2002). This is done in a highly controlled way to
keep digestibility at a maximum, while achieving a good reduction in organics. Keeping a high content of
digestible aluminium requires avoidance of thermal deactivation of dehydrated Gibbsite (Hollitt, Kisler,
& Raahauge, 2002). The extent of deactivation is not measurable, even by NMR, and is seen only in a
decrease in digestion performance (Hollitt, Kisler, & Raahauge, 2002).
Q3.
Pre-Desilication
The pre-desilication step in the refining process forms insoluble compounds from the reactive silica in
the bauxite. To form these compounds, both NaOH and Al2O3 is consumed, with larger amounts being
consumed for greater amounts of reactive silica. The NaOH is a valuable reagent and is very important
for the digestion stage. The sample from Location A has double the amount of silica when compared to
Location B, so the bauxite from Location B is more suitable for this step of the process. The reactivity of
the samples is not specified however, and it is possible that the ratio of reactive silica may be different
from the ratio of the overall amount. Further wet chemistry methods could help to further describe the
reactivity of the silica in the samples.
Digestion
The digestion stage breaks down both the Gibbsite (Al(OH)3) and Boehmite-diaspore mix (AlO(OH)) into
Bayer liquor. Gibbsite is much easier to break down than Boehmite-diaspore, so the sample form
Location A will be much easier to process. The higher ratio of Boehmite-diaspore in the sample from
Location B will require more NaOH reagent, increasing costs of the process. The total percentage of
aluminium found in the sample from Location B is larger however, which may decrease the extra costs in
the digestion stage by producing more aluminium at the end of the process. Several side reactions also
take place in this stage. As Location B has a greater concentration of organics, it will produce a greater
concentration of VOCs released during the process. This may increase the process cost of this stage, but
this is probably negligible as the systems used to treat these are relatively cheap to scale. The higher
organic concentration in Location B will also increase the consumption of the oxygen as they react to
produce hydrogen and other gasses, which results in reducing conditions. Another major pollutant
released in this stage is mercury, and an assessment of the mercury concentrations in the two samples
could help to correctly asses the best bauxite source to use.
Clarification
The clarification stage separates iron oxides (Fe2O3), titanium oxides (TiO2) and silicates formed from
pre-desilication from the Bayer liquor. Location A contains a higher concentration of Fe 2O3, and a higher
concentration of silicates (assuming the reactivity is similar in both samples). The larger concentrations
of these particulates will mean larger clarification vessels, an increase in the amounts of flocculants
required to help precipitate the compounds, larger filtration and drying vessels, and larger equipment to
deal with the dried cake by-product. The amount of waste (red mud) will also be greater for the sample
from Location A.
Remaining Stages and Conclusion
The remaining stages in the Bayer process are practically the same for the bauxite from both sources, as
the silicates, Gibbsite and Boehmite-diaspore, iron oxide and titanium oxide, and organics have all been
removed from the process. After the first stages of processing the only difference in the product at this
stage is the concentration of aluminium in the feed, which should be greater for the bauxite from
Location B due to the higher initial concentration.
The source of Bauxite which is recommended is Location A, as the high ratio of Gibbsite to Boehmitediaspore will greatly decrease the cost of the process in the digestion stage. Although the bauxite from
this stage will result in a greater amount of red mud produced, the concentration of VOCs and the
reducing effect from other organics will be much lower (less than 50% of Location B). However, if a
higher yield of aluminium was required, and the increase to the cost of the process was acceptable to
achieve this, then the bauxite from Location B may be the only suitable choice.
References
Hollitt, M., Kisler, J., & Raahauge, B. (2002). THE COMALCO BAUXITE ACTIVATION PROCESS. Proceedings
of the 6th International Alumina Quality Workshop. Brisbane: Rio Tinto Limited.
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