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<strong>The</strong> <strong>Effects</strong> <strong>of</strong> <strong>Drum</strong> <strong>Speed</strong>, <strong>Shake</strong> <strong>Frequency</strong> <strong>and</strong> <strong>Shake</strong> <strong>Amplitude</strong> Combinations<br />

on Cleaning <strong>of</strong> Lignite Fines by Multi Gravity Separator<br />

Derya Oz Aksoy, Sabiha Koca<br />

Eskisehir Osmangazi University, Eskisehir, Turkey.<br />

Huseyin Koca<br />

Anadolu University, Eskisehir, Turkey.<br />

ABSTRACT: Significant amounts <strong>of</strong> fine coal are lost every year all over the world, because modern<br />

processing techniques are unable to recover very fine materials. Moreover many coals also contain high<br />

levels <strong>of</strong> sulphur <strong>and</strong> ash, which results in particulate matter <strong>and</strong> sulphur dioxide emissions when these<br />

materials are burned in coal fired power stations. <strong>The</strong>se emissions cause severe environmental pollutions<br />

<strong>and</strong> have to be reduced to an acceptable level. Physical processing methods are utilized widely to clean<br />

lignite fines. Gravity concentration techniques are preferred because <strong>of</strong> cheapness <strong>and</strong> easiness. Multi<br />

gravity separator is one <strong>of</strong> the recently designed gravity concentration device <strong>and</strong> preferred in fine coal<br />

cleaning due to its high performance. <strong>The</strong> variables <strong>of</strong> multi gravity separator such as drum speed, shake<br />

frequency <strong>and</strong> shake amplitude affect the separation performance significantly. In this work, the<br />

combinations <strong>of</strong> these parameters were studied to determine the optimum conditions <strong>of</strong> separation.<br />

INTRODUCTION<br />

In order to improve the recovery <strong>of</strong> fine coal, <strong>and</strong> at the same time to reduce the sulphur <strong>and</strong> ash content to<br />

an acceptable level, a number <strong>of</strong> fine coal cleaning techniques are available. Cleaning <strong>of</strong> coal by physical or<br />

chemical methods prior to combustion; Removing SO2 gasses by post-combustion control methods;<br />

Synthetic fuel production; <strong>and</strong> removing SO2 during combustion techniques can be utilized for this purpose<br />

(Rowson, 1986).<br />

Amongst these methods cleaning <strong>of</strong> coal prior to combustion involves either physical or chemical<br />

techniques or a combination <strong>of</strong> these. Physical processing methods such as gravity concentration are used in<br />

coal preparation plants widely despite their low efficiency particularly on desulphurization (Khory, 1981;<br />

Shah et al., 2002). Gravity concentration methods are the cheapest therefore they are preferred for economic<br />

reasons. <strong>The</strong> major limiting factor in gravity concentration is the dependence on particle size <strong>of</strong> coal. Pyritic<br />

sulphur is generally disseminated finely <strong>and</strong> can be liberated only by fine grinding. <strong>The</strong>refore fine coal<br />

cleaning should be applied.<br />

Multi Gravity Separator (MGS) was originally designed <strong>and</strong> used in fine metallic minerals<br />

concentration during 1990’s (Chan et al., 1991; Ozdag, et al., 1993, Udaya Bhaskar, et al., 2002). <strong>The</strong>n<br />

MGS was applied to fine coal cleaning (Erdem et al., 2008, 2010; Koca et al., 2000; Oz et al., 2009).<br />

MGS can increase gravity force up to 25 g that improves its ability to process finer materials<br />

<strong>Drum</strong> speed, shake frequency, shake amplitude, washwater flowrate <strong>and</strong> tilt angle are the most<br />

important variables that affect the separation <strong>of</strong> minerals in a MGS. As the particle size <strong>of</strong> the minerals<br />

gets finer, the interaction between these parameters gets more complicated <strong>and</strong> reduces the efficiency <strong>of</strong><br />

the cleaning process. <strong>The</strong>refore studies were conducted to determine the interactions <strong>of</strong> these variables.<br />

In another work done by the same authors, washwater flowrate <strong>and</strong> drum speed combinations <strong>of</strong> the<br />

MGS was studied in details to improve the performance <strong>of</strong> the process (Aksoy, et al., 2011). In this work,<br />

other important parameters <strong>of</strong> the MGS, namely shake frequency <strong>and</strong> shake amplitude were studied to<br />

determine the interaction with drum speed.


MATERIAL AND METHOD<br />

Lignite samples were taken from a nearby open pit coal mine. Samples were dry ground in open air <strong>and</strong><br />

ground to -0.212 mm in size. <strong>The</strong> ash content <strong>of</strong> the lignite sample is 42.56 %.<br />

<strong>The</strong> Mozley laboratory C 900 MGS were used in the experimental work. Its structure <strong>and</strong> operating<br />

conditions were given elsewhere (MGS Application Guide 1991; Chan et al. 1991).<strong>The</strong> feed to the MGS<br />

was prepared by mixing 500 grams <strong>of</strong> dry sample with one liter <strong>of</strong> water that gives 33 % solids<br />

concentration (by weight). <strong>The</strong> mixture was stirred continuously to maintain uniform suspension. <strong>The</strong><br />

MGS variables were adjusted at the required level as per the experimental design. <strong>The</strong> feed slurry was<br />

then fed to the MGS feed vessel at the required flow rate as the MGS was in operation. <strong>The</strong> separator was<br />

kept running until the material flow was finished, which took about 5 minutes, <strong>and</strong> MGS was stopped.<br />

Upper cover <strong>of</strong> the separator was removed, <strong>and</strong> remaining material in the drum was taken into equivalent<br />

fractions. Heavy product, which was collected through front launder, referred to as tailings, <strong>and</strong> light<br />

product, which was collected through back launder, referred to as concentrate.<br />

RESULTS AND DISCUSSION<br />

<strong>The</strong> effects <strong>of</strong> drum speed, shake frequency <strong>and</strong> shake amplitude combinations on the cleaning <strong>of</strong> lignite<br />

fines were studied. <strong>The</strong> other experimental conditions were kept constant as following:<br />

<strong>Drum</strong> speed : 220-260 rpm<br />

<strong>Shake</strong> frequency : 4-5 cps<br />

<strong>Shake</strong> amplitude : 10-20 mm<br />

Washwater flowrate : 1 l/min<br />

Feed density : 33 %<br />

Feeding duration : 90 sec<br />

Washing duration : 5 min<br />

Tilt angle : 0 o<br />

Results are given in graphs in terms <strong>of</strong> ash content <strong>and</strong> combustible recovery in the concentrate<br />

fraction. <strong>The</strong>re are a number variables which affect the separation <strong>of</strong> minerals in a multi gravity separator.<br />

It is thought that drum speed, shake frequency <strong>and</strong> shake amplitude are the most important ones. <strong>The</strong>re<br />

should be an optimum combination <strong>of</strong> these variables for a given minerals mixture.<br />

<strong>The</strong> effects <strong>of</strong> drum speed <strong>and</strong> shake frequency at 10, 15 <strong>and</strong> 20 mm shake amplitude are given in<br />

Figure 1-3.<br />

Ash, %<br />

44<br />

42<br />

40<br />

38<br />

36<br />

34<br />

32<br />

4 cps<br />

4.5 cps<br />

5 cps<br />

210 220 230 240 250 260 270<br />

<strong>Drum</strong> <strong>Speed</strong>, rpm<br />

75<br />

70<br />

65<br />

4 cps<br />

4.5 cps<br />

5 cps<br />

210 220 230 240 250 260 270<br />

<strong>Drum</strong> <strong>Speed</strong>, rpm<br />

(a) (b)<br />

Figure 1. <strong>The</strong> effects <strong>of</strong> drum speed <strong>and</strong> shake frequency on ash content (a) <strong>and</strong> combustible recovery (b)<br />

at 10 mm shake amplitude.<br />

Combustible Recovery, %<br />

100<br />

95<br />

90<br />

85<br />

80


(a) (b)<br />

Figure 2. <strong>The</strong> effects <strong>of</strong> drum speed <strong>and</strong> shake frequency on ash content (a) <strong>and</strong> combustible recovery (b)<br />

at 15 mm shake amplitude.<br />

Ash, %<br />

44<br />

42<br />

40<br />

38<br />

36<br />

Ash, %<br />

44<br />

42<br />

40<br />

38<br />

36<br />

34<br />

210 220 230 240 250 260 270<br />

<strong>Drum</strong> <strong>Speed</strong>, rpm<br />

4 cps<br />

4.5 cps<br />

5 cps<br />

4 cps<br />

4.5 cps<br />

5 cps<br />

34<br />

210 220 230 240 250 260 270<br />

<strong>Drum</strong> <strong>Speed</strong>, rpm<br />

Combustible Recovery, %<br />

85<br />

4 cps<br />

4.5 cps<br />

5 cps<br />

80<br />

210 220 230 240 250 260 270<br />

<strong>Drum</strong> <strong>Speed</strong>, rpm<br />

(a) (b)<br />

Figure 3. <strong>The</strong> effects <strong>of</strong> drum speed <strong>and</strong> shake frequency on ash content (a) <strong>and</strong> combustible recovery (b)<br />

at 20 mm shake amplitude.<br />

<strong>Drum</strong> speed <strong>of</strong> the MGS is one <strong>of</strong> the most important parameter that affects the separation<br />

significantly. <strong>Drum</strong> speeds between 160 <strong>and</strong> 300 rpm increase the g force from 7 to 25 g at the internal<br />

drum surface. <strong>The</strong> increased g force allows the separation <strong>of</strong> minerals that have smaller density<br />

differences <strong>and</strong> finer particle sizes (MGS Application Guide, 1991; Chan et al., 1991).<br />

<strong>The</strong> shake amplitude <strong>and</strong> shake frequency are important both in mechanism <strong>of</strong> bed dilation <strong>and</strong><br />

stratification, <strong>and</strong> for particle transportation. (Burt, 1984). <strong>The</strong> separation <strong>of</strong> particles in the drum takes<br />

place under the effects <strong>of</strong> shearing forces. Changes in amplitude <strong>and</strong> shake frequency <strong>of</strong> the MGS affect<br />

these forces as well as separation significantly. It was claimed in literature that there should be an<br />

optimum combination <strong>of</strong> shake amplitude <strong>and</strong> shake frequency for a given mineral mixtures (Ozdag et al.,<br />

1993).<br />

As can be seen from Figures 1-3, ash content <strong>of</strong> the concentrates decreased significantly with an<br />

increase in the drum speed at all studied combinations. <strong>The</strong> decrease in ash content in the concentrate was<br />

attributed to the increased g force at the internal drum surface. It should be noticed that separation was<br />

very poor at low drum speeds <strong>and</strong> most <strong>of</strong> the material was reported to the lights fraction. As the drum<br />

speed increases, the quality <strong>of</strong> the separation improves that causes ash reduction in the concentrate. This<br />

also causes the decrease in combustible recovery in the concentrate. <strong>The</strong>refore 260 rpm drum speed was<br />

chosen as optimum value.<br />

Longer amplitude causes more material to report the lights fraction. <strong>The</strong>refore, an increase in shake<br />

amplitude increases both ash content <strong>and</strong> combustible recovery significantly. <strong>Shake</strong> frequency affected the<br />

Combustible Recovery, %<br />

100<br />

95<br />

90<br />

100<br />

95<br />

90<br />

85<br />

80<br />

4 cps<br />

4.5 cps<br />

5 cps<br />

75<br />

210 220 230 240 250 260 270<br />

<strong>Drum</strong> <strong>Speed</strong>, rpm


esults in a different manner. At the shortest amplitude, lower frequency produced the best results while<br />

higher frequency produced better results at higher amplitudes.<br />

CONCLUSIONS<br />

<strong>Drum</strong> speed, shake frequency <strong>and</strong> shake amplitude are the most important variables that affect the<br />

separation <strong>of</strong> minerals in a MGS. As the particle size <strong>of</strong> the minerals gets finer, the interaction between<br />

these parameters gets more complicated <strong>and</strong> reduces the efficiency <strong>of</strong> the cleaning process. <strong>The</strong>refore<br />

studies were conducted to determine the interactions <strong>of</strong> these variables. After MGS experiments, the<br />

optimum conditions were determined as drum speed <strong>of</strong> 260 rpm, 10 mm shake amplitude <strong>and</strong> 4 cps shake<br />

frequency.<br />

At optimum conditions, ash content <strong>and</strong> combustible recovery <strong>of</strong> the concentrate were obtained as<br />

32,92% <strong>and</strong> 77,93%, respectively.<br />

<strong>The</strong> results <strong>and</strong> discussions indicate that drum speed affects the separation quality significantly. Higher<br />

drum speed gives the better results at all studied combinations. <strong>The</strong>re is a strong relationship between<br />

shake amplitude <strong>and</strong> shake frequency. Better results were obtained at slow frequency when amplitude was<br />

short. While the amplitude was longer, higher frequency produced better results.<br />

REFERENCES<br />

Aksoy, O. D., Koca, SD. And Koca, H., 2011. <strong>The</strong> <strong>Effects</strong> <strong>of</strong> Washwater Flowrate <strong>and</strong> <strong>Drum</strong> <strong>Speed</strong><br />

Combinations on Cleaning <strong>of</strong> Lignite Fines. Fifth International Conference on Clean Coal<br />

Technologies CCT2011, May, 8-12, 2011, Zarogoza, Spain.<br />

Burt, O. R., 1984. Gravity Concentration Technolgy, Amsterdam, <strong>The</strong> Nedherl<strong>and</strong>s, Elsevier Science<br />

Publishers B. V., p. 605.<br />

Chan, B. S. K., Mozley, R. H. <strong>and</strong> Childs, G. J. C., 1991. Extended Trials with the High Tonnage Multi<br />

Gravity Separator. Minerals Engineering, 4, p. 489-496.<br />

Erdem, A., Olgun, Z., Gulmez, A., Altun, O., Gitmez, A., Oteyaka, B. <strong>and</strong> Koca, S. 2008. Beneficiation<br />

<strong>of</strong> Lignites by Means <strong>of</strong> Shaking Table, MGS <strong>and</strong> Flotation, Project report 2, Project No. 106G056,<br />

MTA, Ankara.<br />

Erdem, A., Olgun, Z., Gulmez, A., Altun, O., Gitmez, A., Oteyaka, B. <strong>and</strong> Koca, S. 2010. Benefications<br />

<strong>of</strong> Coal Fines from Tailing Ponds <strong>of</strong> Tuncbilek Washing Plant. In Proceedings <strong>of</strong> the XXV.<br />

International Mineral Processing Congress, September, 6-10, Brisbane, Australia, 2010, p. 3737-3742.<br />

Khory, D.L., 1981. Coal Cleaning Technology, Khory, D.L. (ed.), New Jersey: Noyes Data Corp., p.367.<br />

Koca, H., Koca, S. <strong>and</strong> Karaoglu, M., 2000. Recovering <strong>of</strong> Fine Coal Particles from Tailing Ponds <strong>of</strong><br />

Ankara- Alpagut- Dodurga Coal Washing Plant. In Proceedings <strong>of</strong> the XI. International Conference on<br />

Environmental Issues <strong>and</strong> Management <strong>of</strong> Waste in Energy <strong>and</strong> Mineral Production SWEMP 2000,<br />

May 30-June 2, 2000, Calgary, Alberta, Canada, p. 117-121.<br />

MGS Application Guide, 1991. How to Get the Best from Your C-900 MGS. No.1, Richard Mozley Ltd,<br />

Cornwall, UK.<br />

Oz, D., Koca, S. <strong>and</strong> Koca, H., 2009. <strong>The</strong> Utilization <strong>of</strong> Unsaleable Lignite Fines at Eskişehir Koyunağılı<br />

Region Lignite Deposits. Physical Separation 09, June, 16-17, 2009, Falmouth, Engl<strong>and</strong>.<br />

Ozdag, H., Ucbas, Y. <strong>and</strong> Koca, S., 1993. Enrichment <strong>of</strong> Chromite Ore by Means <strong>of</strong> multi-Gravity<br />

Separator, Geosound, 23, p.167-176.<br />

Rowsan, N. A., 1986. Desulphurisation <strong>of</strong> Coal by Microwave Energy, Ph.D. thesis, Leeds University,<br />

UK.<br />

Shah, C.L., Abbott, J. A., Miles, M. J., Xuejun, L. <strong>and</strong> Jianping, X., 2002. Sulphur Reduction Evaluation<br />

<strong>of</strong> Selected High-Sulphur Chinese Coals. Fuel, 81, p. 519-529.


Udaya Bhaskar, K., Govindarajan, B., Barnwal, J. P., Venuggopal, R., Jakhu, M. R. <strong>and</strong> Rao, T. C., 2002.<br />

Performance <strong>and</strong> Modelling Studies <strong>of</strong> an MGS for Graphite Rejection in a Lead Concentrate.<br />

International Journal <strong>of</strong> Mineral Processing, 67, p. 59-70.

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