In this research, the efficiencies on rare-earth elements extractions as functions of pH levels,
extractant concentration, O/A ratio, metal concentration were investigated. Based on that, the
proper conditions of REEs recovery were set up to investigate the efficiency of Y, Eu and Tb
recovery from acid leach solution that was leached from fluorescent powder of discarded
fluorescent lamps in hydrochloric acid. The grade of the final product was 94.2 % (for
yttrium) and 93.8 % (for terbium and europium group).
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Vietnam Journal of Science and Technology 56 (2C) (2018) 133-139
PRELIMINARY STUDY ON SEPARATION OF RARE EARTH
METALS FROM LEACH SOLUTION OF DISCARDED
FLUORESCENT POWDER BY SOLVENT EXTRACTION
Nguyen Duc Quang, Ha Vinh Hung*, Vu Minh Trang, Le Huy Viet,
Huynh Trung Hai
School of Environmental Science and Technology, Hanoi University of Science and Technology,
1 Dai Co Viet, Ha Noi
*Email: hung.havinh@hust.edu.vn
Received: 20 May 2018; Accepted for publication: 22 August 2018
ABSTRACT
Discarded fluorescent lamps were considered as hazardous waste in Vietnam (code is
160106). However, its composition contained valuable rare earth metals, which can be recycled
and recovered by leaching and solvent extraction processes. The present study sought to define
the conditions of separation for rare earth elementals (REEs) from acid leach solution by solvent
extraction using PC88A. The acid leach solution was obtained from leaching of fluorescent
powder. Efficiencies on REEs extractions as functions of pH levels, extractant concentration,
O/A ratio, metal concentration were investigated. For pH values greater than 0.0 and less than
1.0, the orders of the yields extraction were determined: yttrium > terbium > europium >
aluminum and calcium. The best separation circuit included four-stage counter current extraction
for yttrium separation with 20 %v/v PC88A in kerosene (O/A = 1/1, room temperature, 20 min
of contact, pH of 0.38) and stripping step with 3 M HCl acid (O/A = 1/1, room temperature,
30 min of contact). After yttrium separation, the leach solution was extracted at pH of 0.98 in the
same other conditions with two-stage counter current extraction to recover terbium and
europium group. The final recovery from leach liquor was higher than 98 % and the grade of the
final product was 94.2 % (for yttrium) and 93.8 % (for terbium and europium group).
Keywords: rare earth, recovery, fluorescent lamp, solvent extraction, PC88A.
1. INTRODUCTION
Legally, the discarded fluorescent lamps are considered as hazardous waste (code 160106
as classified in Circular 36/TT-BTNMT on management of hazardous wastes), due to the Hg
vapor and fluorescent powder composition. Nevertheless, it also contain Rare Earth Elements
(REEs), which are used as optical composition of fluorescent powder. Modern fluorescent lamps
use a mix of red (Y2O3: Eu3+), green (CeMgAl10O17: Tb3+) and blue (BaMgAl10O17: Eu2+)
phosphors to generate white light [1]. Therefore, light color of the lamp depends on the REEs
presented in the fluorescent powder. In red light lamp, Y2O3 is taken 85.3-90.0 % of fluorescent
Ha Vinh Hung, et.al.
134
powder and Eu2O3 is about 6.8-7.6 % [2]. In green light lamp, CeO2 is 11.5-15 % and Tb4O7 is
6.2-7.4 %. The number is 2.0-2.2 % for Eu2O3 in blue light lamp. The weight of Y2O3 in a lamp
ranges from 0.005 g/unit (in case of light emitting diodes) to 0.70-0.77 g/unit (in case of
compact fluorescent lamp) and even up to 1.1-1.2 g/unit in case of linear fluorescent lamp [3].
The phosphors mixture accounts for 2 wt% of a typical 40 W fluorescent lamp (4–6 g powder)
[1].
Hydrometallurgical methods have been studied for the recovery of REEs in fluorescent
lamps. Leaching, precipitation and solvent extraction were investigated completely. Major
solvents are researched including HCl [1, 4, 5], H2SO4 [4-6], HNO3 [7-8]. The extraction
solvents were mostly including Tributyl phosphate, 2- ethylhexyl phosphoric acid, mono 2-
ethylhexyl ester and Di (2-ethylhexyl) phosphoric acid [9, 10]. For the precipitation, oxalic acid
and ammonium bicarbonate are widely used [6]. The common efficiency of these researches is
more than 95 %.
In Vietnam, the fluorescent lamps are now only treated as a hazardous waste in 24 licensed
facilities with the average capacity of 0.2 ton/day. All of the treatment lines are focused on
treatment/recovery Hg vapor, aluminum part and glass, but not recycling of fluorescent powder.
Nevertheless, the research on recovery REEs from fluorescent powder is rare. In our previous
research, HCl has been used to leach Y and Eu from the fluorescent powder with 100 % of Y
yield and 99 % of Eu [11]. This research focuses on the extraction of REEs using PC88A in
kerosene from acid leach solution obtained from leaching of fluorescent for the efficient
recycling of fluorescent lamps in Viet Nam.
2. MATERIALS AND METHODS
2.1. Materials and reagents
The experiments were conducted by using the acid leach solution from discarded
fluorescent powder. The composition of REEs and others have been determined by ICP-MS and
shown in Table 1. The PC88A in kerosene was used as extractant. NaOH solution (1M) was
added to adjust the pH values of the leach solution as requested by the experimental tests.
Table 1. Chemical composition of the leach solution.
Element Y Eu Tb Al Ca
Concentration (mg/L) 511.90 55.01 32.60 153.00 29770
2.2. Solvent extraction tests
Loading of metals from REE-containing leachate was conducted using PC88A in kerosene.
The solutions were mixed by separatory funnel shaker (Lab companion RS-1, Korea) having six
separating funnels. The investigated factors were pH values, extractant concentration, O/A ratio,
metal concentration in order to define the optimum conditions. Each test was performed by
shaking with speed of 250 rpm (vertical reciprocating) for 20 min in separatory funnel, the 100
ml volume of aqueous phase and organic phase at ambient temperature. After contacting time,
the funnel-containing samples were rested on the rack for separation. Stripping with 2 M
hydrochloric acid solutions was investigated under similar conditions. The equilibrium pH of
Preliminary study on separation of rare earth metals from leach liquor of discarded fluorescent
135
aqueous phase was determined by titration of H+ ion concentration. The amounts of metals
extracted/stripped were calculated using mass balance, by measuring their concentration in the
aqueous phases before and after phase contact by ICP-MS [11] (Elan 9000 – Perkin Elmer).
3. RESULTS AND DISCUSSIONS
3.1. Effect of equilibrium pH on extraction efficiency
The investigation results on the effect of pH on the extraction efficiency are shown in Fig. 1.
It is found that, for each metal ion the extraction efficiency increases as the pH increases and
there is a sudden change within a narrow pH range: Y3+ ion from (-0.18) to 0.56; Tb3+ ion from
0.16 to 0.86; and Eu3+ ion from 0.57 to 1.14. It can be explained that the extraction reaction is
the reciprocal reaction and following the Le Chatelier’s principle, when the pH of the solution
increases, the concentration of H+ should be decreased and the equilibrium moves to generate
RE(HX2)3or by the extraction reaction:
RE3+w + 3H2X2or ↔ RE(HX2)3or + 3H+w (1)
In addition, it is found that, at pH ≤ 1.09 almost impurities (Al3+ and Ca2+ ions) are not
extracted, the extraction efficiency is about 11% and <1.6%, respectively.
The coefficient of thermal equilibrium dynamic of extraction reaction is calculated as:
Keq = = D* (2)
where: RE3+ denotes rare-earth element; H2X2 is PC88A solvent; w denotes water phase; or
denotes organic phase and D is distribution coefficient, D=[RE(HX)3or]/[RE3+w].
Depending on the properties of the metal, the dependence of the distribution coefficient D
on the pH of each metal ion is not the same. This behavior can be attributed to the difference of
stability constants of metal complexes with PC88A. Thus, pH control is the most basic
procedure for separating metals. From this result in Fig. 1 also showed that at pH of 0.38 the
extraction efficiency of Y, Tb, Eu, Al and Ca is about 79 %, 35 %, 11 %, 1.6 % and <1.6 %,
respectively, thus it can be selected the pH of 0.38 for Y separation in first stage. Similar, after
separation of Y, it can be selected the pH of 0.98 for separation of Tb and Eu group in second
stage due to the extraction efficiency of Tb, Eu, Al and Ca is about 96 %, 87 %, 11 % and
<1.6 %, respectively.
3.2. Effect of extractant ratio on extraction efficiency
The investigating result on extractant ratio Ror (ml/ml) on the extraction efficiency is shown
in Fig. 2. It is found that at the beginning of reaction, when Ror increases, the efficiency increases
rapidly. But as the percentage of solvent in the solvent increases, the efficiency of the process
has slowly increased up to balance point. At the initial time, the concentration of REEs exceeds
the extraction capacity of the extractant. It is clear that, PC88A ratio was increased synonymous
with the increasing of [HX2]- radical, lead to the number of [HX2]- – metal ion pairs increased so
the efficiency was increased. However, the metal ion concentration was fixed so that the
efficiency of the process has slowly increased up to the balance point.
Ha Vinh Hung, et.al.
136
Figure 1. Effect of equilibrium pH on extraction
efficiency.
Figure 2. Effect of PC88A ratio on extraction
efficiency.
3.3. Effect of REEs concentration in the acid leach solution
Figure 3. Effect of extractant concentration on
extraction efficiency of Y.
Figure 4. Effect of extractant concentration on
extraction efficiency of Eu and Tb.
Figure 5. Effect of organic/acid leach solution
phase ratio on extraction efficiency.
Figure 6. Effect of rate of organic/ acid leach
solution phase ratio on organic phase after
extraction.
Preliminary study on separation of rare earth metals from leach liquor of discarded fluorescent
137
Figure 7. Determination of number of Y extraction
and stripping step.
Figure 8. Determination of number of Eu and Tb
extraction and stripping step.
Figure 3 and Fig. 4 show that the extraction efficiency slightly decreases when metal
concentration in the acid leach solution increases. It is due to (1) the limited concentration of
extractant; (2), the forming of H+ ion is increased when metal concentration in the acid leach
solution increases, lead to the decreasing of efficiency; and (3), the increasing of metal
concentration will cause the decreasing of activity degree of REEs ion, which cause the
decreasing of efficiency.
3.4. Effect of organic/acid leach solution ratio
The increase of organic/acid leach solution (O/A) rate (i.e. increase of [H2X2]) will
increase the extraction efficiency as follow the Le Chatelier’s principle in Equation 1, as shown
in Fig. 5. Nevertheless, it leads to the decrease of REEs concentration in the organic phase (Fig.
6), and thus, cause the decrease of recovery REEs. This behavior is similar to the case in
subsection 3.2.
3.5. Recovery REEs from acid leach solution
The determination of extraction and stripping step for REEs recovery is shown in Fig. 7
and Fig. 8, based on the investigation results.
3.5.1. Yttrium extraction
Table 2. REEs and metal concentrations in stripping solution of yttrium.
Element Y Eu Tb Al Ca
Concentration in stripping solution (mg/L) 511.43 5.88 25.19 <0.06 0.558
Purity (% of cations) 94.2 1.1 4.6 0 0.1
Based on the investigation results, the proper separation circuit is selected included four-
stage counter current extraction for yttrium separation with 20 %v/v PC88A in kerosene
(O/A = 1/1, room temperature, 20 min of contact, pH of 0.38). The extract after extraction was
stripped a stage with 3 M HCl acid, which equals with pH -0.477 (O/A = 1/1, room temperature,
30 min of contact). The composition of yttrium stripping is shown in Table 2.
Ha Vinh Hung, et.al.
138
3.5.2. Europium and terbium extraction
After yttrium extraction, the raffinate was extracted at pH of 0.98 in the same other
conditions with two-stage counter current extraction to recover terbium and europium group.
The extract phase was stripped a stage with 3 M HCl acid, the composition of europium and
terbium group stripping is shown in Table 3.
Table 3. REEs and metal concentrations in stripping solution of terbium and europium group.
Element Y Eu Tb Al Ca
Concentration in stripping solution (ppm) 0.32 49.00 6.11 0.41 2.92
Purity (% of cations) 0.5 83.4 10.4 0.7 5.0
4. CONCLUSION
In this research, the efficiencies on rare-earth elements extractions as functions of pH levels,
extractant concentration, O/A ratio, metal concentration were investigated. Based on that, the
proper conditions of REEs recovery were set up to investigate the efficiency of Y, Eu and Tb
recovery from acid leach solution that was leached from fluorescent powder of discarded
fluorescent lamps in hydrochloric acid. The grade of the final product was 94.2 % (for
yttrium) and 93.8 % (for terbium and europium group).
Acknowledgement. The authors wish to acknowledge Ministry of Education and Training of Vietnam for
financially supporting under project entitled "Studying on Yttrium and Europium recovery technology in
waste fluorescent lamps – Code: B2017-BKA-43".
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