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Journal of the Southern African Institute of Mining and Metallurgy

On-line version ISSN 2411-9717
Print version ISSN 2225-6253

J. S. Afr. Inst. Min. Metall. vol.118 n.8 Johannesburg Aug. 2018

http://dx.doi.org/10.17159/2411-9717/2018/v118n8a12 

PAPERS OF GENERAL INTEREST

 

Evaluation of alternative solid media for coal beneficiation using an air dense-medium fluidized bed

 

 

K.M. Chagwedera; S.O. Bada; R.M.S. Falcon

Clean Coal and Sustainable Energy Research Group, Faculty of Engineering and the Built Environment, University of the Witwatersrand, South Africa

 

 


SYNOPSIS

A study was carried out to identify alternative dense media with potential for use in coal beneficiation in South Africa. Magnetite, pyrrhotite, silica sand, granulated blast furnace slag, and coal discards were tested. Magnetite and pyrrhotite provided the most uniform and stable bed densities, with bed density variation less than 0.7% and standard deviation less than 0.0025 g/cm3. A 100% magnetite bed yielded a product with an ash content of about 20.30% and calorific value of about 25.24 MJ/kg from a feed coal of size fraction -13 +6 mm and ash content of 39.27%. A cleaner coal product containg about 14.50% ash and with calorific value of 27.30 MJ/kg was obtained from a bed of pyrrhotite and magnetite blend at a weight ratio of 40:60. The same blend reduced the total sulphur content from 2.49% in the feed coal to about 0.41% at a cut density of 1.63 g/cm3 at a probable error (Ep) of 0.083. The beneficiation of coal in a pure magnetite bed was not as effective as with the pyrrhotite-magnetite mixed bed.

Keywords: air separation, dense medium, fluidized bed, separation efficiency, bed stability.


 

 

Introduction

South Africa has vast coal reserves and its economy is heavily dependent on this abundant resource for primary energy needs. From the estimated 333.6 Mt of RoM (run-of-mine) produced in 2014, approximately 128.2 Mt was used in the generation of electricity (Prevost, 2015). The demand for coal in South Africa as the primary energy source is unlikely to change in the near future.

The Witbank coalfield in Mpumalanga Province supplies 50% of South Africa's saleable coal. However, the reserves are near exhaustion and the remaining coal is of poor quality. This has led to the development of the Waterberg coalfield, which is estimated to contain about 40 to 50% of South Africa's remaining coal (Hancox and Götz, 2014). The main challenge facing the Waterberg region is a lack of water, which might be an obstacle in implementing the conventional wet beneficiation techniques.

This investigation into utilizing dry beneficiation techniques was motivated by the large quantities of water used or lost during coal preparation, and the cost of managing and treating the large volumes of aqueous slurries generated during the wet process. In addition, coal beneficiated by dry methods retains a higher thermal heating value (Dwari and Rao, 2007). Air dense-medium fluidized bed (ADMFB) processes have been investigated for a number of decades and some of the results were patented as early as 1926 (Fraser and Yancey, 1926). The foundation for the industrial application of the ADMFB coal separation was based on studies conducted by different authors over the past decades. Zhao et al. (2016) present some of the most recent development in the industrial application of the ADMFB in the form of a large-scale (40-60 t/h) plant.

The solid medium material used in the ADMFB separator is one of the key factors for efficient coal separation. Magnetite has been widely used by other investigators. However, the demand for magnetite has increased because of its use in other industries such as steelmaking and catalysis, besides conventional wet coal beneficiation. In addition, the cost and future supply are of concern to the coal industry (Honaker and Bimpong, 2009). Some of the alternative solid media that have been investigated for use in the ADMFB include silica sand, silica-zircon mixtures, magnetic pearls, and paigeite. Azimi et al. (2013) used silica sand to achieve a recovery of 95.63%, and clean coal ash content of 10.6%, from a feed coal of 14.4% ash, at a separation efficiency of 15.29%. Firdaus et al. (2012) used a bed of silica-zircon mixture and produced a clean coal product of about 9.71% ash at an Ep of 0.06, with 77.8% recovery. Similarly, paigeite ore has been used to reduce coal ash content from 22.37% to 9.88% with a yield and Ep of 60.64% and 0.075, respectively (Zhao et al., 2011). Magnetic pearls used by Luo et al. (2007) achieved an Ep value of 0.05, with a coal product of 13.95% ash and yield of about 90.80%.

This study focused on utilizing locally available alternative solid media materials in the ADMFB separator. The media tested include magnetite (4 880 kg/m3), pyrrhotite (2 983 kg/m3), granulated blast furnace slag (2 699 kg/m3), silica sand (2 410 kg/m3), and coal rejects (2 112 kg/m3). The use of pyrrhotite, alone or as a blend with magnetite, for a solid medium in an ADMFB application has not been reported before. Pyrrhotite, which is a reject dumped to tailings in nickel concentration and platinum group metals (PGMs) processing, has a density (approximately 3 g/cm3) suitable for creating a fluidized bed and is known to occur in a magnetic form (Fe7S8), which aids in dense media recovery. These properties make pyrrhotite a potentially suitable dense medium for coal beneficiation in an ADMFB separator.

 

Experimental

Materials

The materials used in this study include the solid media, density tracers, and coal sourced from the Witbank coalfield in South Africa. The solid media were also obtained from different sources within South Africa and prepared in accordance with ISO 3082:2009 into the required size range (-425 +106 Jim) for testing. Density tracers were used instead of coal to determine the best operating parameters and separation efficiency for each of the media utilized. The tracers were cube-shaped particles of -13 +6 mm size range, and within the density range 1.2-2.0 kg/m3. The 100 kg coal bulk sample used for the test was prepared according to ISO 13909:2016 at a particle size range of -13 +6 mm. Batch samples of 1 kg were subsequently used for the float-sink and the dry beneficiation experiments.

Equipment

The fluidized bed (Figure 1) used in this study was constructed from Perspex reinforced with a steel frame of a square cross-section of 40 cm x 40 cm with a height of 60 cm.

 

 

The distributor was made of a canvas material compacted between two sheets of wire mesh. The inlet air into the system was cleaned and dried by passing it through an air filter, and the pressure into the system was maintained at 450 kPa(g). The pressure drop within the bed's cross-sectional area was measured at nine different points using nine probes, each connected to a pressure transducer. The pressure readings were transformed through the transducers into electrical signal 'data' and recorded using an Agilent 34970A data logger.

 

Test method

The fluidized bed was loaded with one dense medium material at a time, with three static bed heights (20, 25, and 30 cm) used for each material. The approximate mass of each material in the fluidized bed is shown in Table I.

 

 

The operating velocity was determined and pressure drop measurements were taken at different points in the bed cross-section (plan view). A total of nine pressure point (A to I) readings were taken at bed heights of 0, 5, 10, 15, 20, 25, and 30 cm) at a rate ot one reading per 500 milliseconds. Pressure drop profiles and density profiles were plotted, as seen in Figure 2. The process parameters such as superficial air velocity and static bed height were optimized through beneficiation tests using density tracers. A superficial air velocity of 12 cm/s, static bed height of 20 cm, and separation time of 20 seconds were established. The solid medium with the best separation efficiency was selected as the dense medium material for coal beneficiation. The tests involved feeding 1 kg of coal into the fluidized bed and performing the separation at the established optimum conditions. A brush and flat scraper (40 cm length) were used to gently remove the medium material at 1 cm intervals. All the coal particles collected from the top of the bed to 10 cm depth were combined and recorded as 'floats', and particles collected from 10-20 cm depth were considered 'sinks'. Each test run was repeated at least three times in order to improve the precision and accuracy of the results.

 

Analytical methods

Particle density was measured using pycnometry according to ISO 125154:2014. The particle size distribution of the samples was measured in accordance with ISO 13320:2009 using a Malvern Mastersizer 2000 laser particle analyser. The Davis tube test (ISO 8833:1989) was used to determine the magnetic content of the medium materials. XRF analysis according to ISO TR 18336:2016 was used to quantify the iron content of the magnetic and nonmagnetic products of the Davis tube test.

Float and sink tests were performed on the feed coal in accordance with ISO 7936:1992 to determine its washability characteristics. The products and discards obtained were subjected to the same test, and the data was used to plot the partition curves for determining the separation efficiency of the process. Ultimate and sulphur analyses of all samples were performed according to ASTM D 5373-02 and ASTM D 4239-05 respectively, using a Leco CHN 628 with add-on 628 S module. Proximate analyses to determine the inherent moisture, ash content, and volatile matter were conducted in accordance with ASTM D-5142, using samples of approximately 1 g. The fixed carbon for the samples is expressed as 100% minus (ash content + volatile matter + moisture content). The calorific value was determined using a Leco AC 500 calorimeter in accordance with ASTM D5865-04.

 

Results and discussion

Coal and solid medium characterization

The physical properties of the media, including particle size distribution (PSD) and magnetic content, are shown in Table II. The Davis tube was used to separate the magnetic and nonmagnetic fractions in the proposed medium materials at settings ranging between 0.5 and 2.0 A. Pyrrhotite was the only medium out of the four proposed media that had both a magnetic and a nonmagnetic fraction, comprising about 30% and 70% respectively.

The results of the physicochemical analyses of the feed coal are depicted in Table II. The RoM coal sample is classified as a very high-ash, low fixed carbon, D3 grade coal with a low volatiles content (Code 3) coal according to the South African Standard Classification of Coals.

The XRF analysis conducted on the feed pyrrhotite and magnetic and nonmagnetic fractions from the Davis tube test showed that the magnetic fraction has the highest concentration of iron (Table III). This test further supports the utilization of pyrrhotite as a medium that can be used with magnetite for dense medium coal separation.

Bed fluidization characteristics

Fluidization characterization tests were carried out to determine the fluidization behaviour for each solid medium. Figure 2 shows an illustration of the pressure drop profile for two of the nine points in the bed, with magnetite as the dense medium material at 20 cm static bed height.

The equations below were used to calculate the bed density from the pressure drop profiles (Chikerema, 2011):

where

The gradient of the pressure drop against bed height plot gives the bed density:

where 104 is a conversion factor.

The density was determined for each pressure point in the bed and the data was tabulated as shown in Table IV.

Uniformity of the bed density is an important indicator of the stability of a fluidized bed and consequently its ability to provide an efficient separation. Efficient dry separation conditions in an ADMFB are obtained when a stable dispersion, fluidization, and micro-bubbles are achieved. It is very important that the bed density is well distributed in three-dimensional space and does not change with time (Chen and Wei, 2003). The density distribution for different points in the bed utilized in this study was determined by plotting the bed density attained against the bed height. The distribution was analysed vertically per each sampling point and horizontally per each bed level (multiple sampling points).

Figure 3 shows a plot of the vertical distribution of the bed density for two specific pressure points. For pressure point A, the density range was 1871-1965 kg/m3 with an even distribution (R2 = 1) from the bottom to the top of the bed, which was the case for point B and other pressure points taken in this study.

The stability and uniformity of the fluidized bed were established by determining the standard deviation for the density distribution (Sp) for each point (Zhang et al., 2014). Sp is given by the following equation:

where

On the other hand, the coefficient of variation (CoV) was also used in this study to further determine the extent of variation of the bed density from its mean at each horizontal bed level. The CoV was calculated by the following equation:

 

 

Table V shows the standard error (Sp), and CoV for bed density at 20 cm bed height of magnetite.

Table V shows that the CoV ranges between 0.33-0.37%, while the Sp is between 2.05-2.41 kg/m3, indicating a very stable and uniform bed under these operating conditions. The same procedure was applied to all the solid media proposed as an alternative to magnetite in this study. The data obtained was used to plot the graph of CoV vs. average bed density, as seen in Figure 4.

Figure 4 was used to select the best solid medium and the static bed height at which the bed density is stable and uniform. Magnetite, pyrrhotite, and GBFS at 20 cm bed height exhibit the most uniform and stable beds, with a coefficient of variation less than 0.7%. However, the GBFS bed had an average density of about 1 000 kg/m3 which, coupled with its lack of magnetism, makes it unsuitable for coal separation as the sole medium but with some potential if blended with magnetite.

ADMFB separator results using magnetite and pyrrhotite ore (-425 +106 μ m)

Magnetite and pyrrhotite were chosen as a solid medium for the initial beneficiation test, using density tracers. Preliminary results with a magnetite bed alone were used as a baseline for comparison. ADMFB separation was conducted using different static bed heights, and a yield of 55% and Ep of 0.40 were achieved with a bed height of 20 cm. This bed height was selected for all subsequent tests. Pyrrhotite alone, with a calculated average bed density of 1300 kg/m3, could not form a bed with an effective cut density for the density tracers (1.2-2.0 kg/m3) tested. Therefore, a blend of pyrrhotite and magnetite at different weight % ratios was tested.

 

 

Density tracer separation with a blend of pyrrhotite/magnetite

An investigation was conducted to determine the influence of different blends of magnetite with pyrrhotite on the ADMFB separation efficiency. The blends were prepared using from 20% to 50% by weight pyrrhotite, with a bed static height of 20 cm. The best separation results for each blend ratio at the optimum conditions are plotted in Figure 6. The optimum blend was at 40% pyrrhotite plus 60% magnetite, with the yield ranging between 53-58% and probable error 0.0530.073. At higher proportions of pyrrhotite, the yield and separation efficiency began to decline. Therefore, the established optimum operating parameters of 12 cm/s superficial air velocity, 20 cm static bed height, and 20 seconds separation time were then utilized for the separation of coal at this optimum blending ratio.

 

 

Coal separation with magnetite and pyrrhotite/ magnetite beds

The RoM material was first subjected to sink/float analysis in order to evaluate the potential of the ADMFB for cleaning coal under different conditions. A 100% magnetite fluidized bed at an optimum operating fluidization velocity Uof of approximately 1.4 Umf and 20 cm static bed height was utilized, and the result compared with that obtained with the blend of pyrrhotite/magnetite.

From the sink and float analysis (Table VI), it can be seen that clean coal of 5.54 % ash with a yield of 1.18 % is obtainable at 1.3 RD. In addition, at an RD of 1.5, clean coal with an ash content of 13.96% and yield of 23.81% was also obtained.

As depicted in Figures 7 and 8, at a cut-point/separation density (p50) of about 1.81-1.82 g/cm3 for the 100% magnetite bed, coal products with a yield and Ep ranging between 60.26-60.89% and 0.070-0.075, respectively were obtained. The product was a clean coal with an ash content of 19.60-20.95% and calorific value of 25.01-25.46 MJ/kg.

 

 

 

 

According to Figure 9, a dense medium of 40% pyrrhotite plus 60% magnetite blend produced clean coal with a error probable (Ep) between 0.080-0.083 and yield ranging between 52.04 and 52.67%.

 

 

The bed's cut-point/separation density (p50) was at 1.63-1.64 g/cm3 (Figure 10). The ash content of the feed coal was reduced from 39.32% to 14.21-14.75% (an overall ash reduction of 62.49-63.86%, while the feed sulphur content was reduced from 2.49% to 0.41-0.42%. The calorific value of the product was 26.77-27.58 MJ/kg.

 

 

The lower ash products obtained with the 40% pyrrhotite bed were a result of the lower p50 of the bed compared to 100% magnetite, for which the p50 was 1.81-1.82 g/cm3. These results indicate that pyrrhotite has potential for use in mixed solid media for ADMFB beneficiation.

 

Conclusion

Pyrrhotite has proved to be the superior dense medium material among the materials proposed as an alternatives to magnetite. The most uniform and stable bed densities were achieved using a blend of pyrrhotite (40%) and magnetite (60%). A cleaner coal product with less ash and sulphur content was obtained from this blend compared to using magnetite alone. Using a 40% pyrrhotite bed, feed ash content was reduced from 39.32% to about 14.50% and the product coal had a calorific value of about 27.30 MJ/kg. The 100% magnetite bed produced a product with an ash content of about 20.30% and calorific value of about 25.24 MJ/kg.

The blending of pyrrhotite, which is considered a reject 'no-cost' material, with magnetite could reduce the cost of operating a coal ADMFB process significantly.

 

Acknowledgments

The authors acknowledge, with thanks, the financial support of Coaltech Research Association (Project No: 4.8.5 c) and the Clean Coal and Sustainable Energy Group of the University of the Witwatersrand. Our gratitude also goes to the University of the Witwatersrand for access to research facilities.

 

References

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Paper received Oct. 2017
Revised paper received May 2018

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