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Rem: Revista Escola de Minas

Print version ISSN 0370-4467

Rem: Rev. Esc. Minas vol.64 no.1 Ouro Preto Jan./Mar. 2011

http://dx.doi.org/10.1590/S0370-44672011000100006 

Metallurgy and materials - Metalurgia e materiais

 

Solvent extraction for metal and water recovery from industrial wastes and effluents

 

Extração por solventes aplicada à recuperação de metais e da água a partir de resíduos industriais e efluentes líquidos

 

Marcelo Borges Mansur

Professor Adjunto do Departamento de Engenharia Metalúrgica e de Materiais, Universidade Federal de Minas Gerais – UFMG E-mail: marcelo.mansur@demet.ufmg.br

 


ABSTRACT

The use of solvent extraction to recover metals and water from industrial residues is highlighted in this work. The method was applied (1) to selectively concentrate Zn from effluents generated by the zinc industry, (2) to separate Zn and Fe from spent pickling effluents produced by the hot-dip galvanizing industry, and (3) to recover Co and Ni from spent batteries. Batch and pilot scale data was used to point out solvent extraction as a feasible method to reuse both metals and water thus resulting in energy savings with reducing environmental impacts, minimizing costs required to transport hazardous materials to waste sites, to replace the discharged wastewater and to produce the raw material that would be previously discharged as wastes.

Keywords: Solvent extraction, metal recovery, environmental.


RESUMO

A aplicação da técnica de extração por solventes para a recuperação de metais e da água a partir de resíduos e efluentes industriais é apresentada nesse trabalho. Os seguintes estudos de caso foram analisados: (1) separação seletiva e concentração de Zn contido em efluentes gerados na indústria de zinco, (2) separação de Zn e Fe presentes em efluentes da indústria de galvanização a quente e (3) recuperação de Co e Ni a partir de baterias de celular descarregadas. Dados obtidos em escala de laboratório e em escala-piloto foram empregados para demonstrar a potencialidade da técnica no tratamento de efluentes, visando à reutilização, tanto dos metais, quanto da água, que seriam inutilizados, resultando em economia de energia com redução de impactos ambientais, além da minimização dos custos relacionados ao transporte de materiais perigosos e manutenção de aterros.

Palavras-chave: Extração por solventes, recuperação de metais, meio ambiente.


 

 

Introduction

The amount of metals contained in hazardous wastes produced worldwide is significant. While adequate disposal of such residues in landfills meets environmental requirements, it results in the loss of valuable metals, energy resources and money. Therefore, recycling is essential to assure sustainability. Technologies that allow both metals and water recovery from toxic residues are urgently needed to help industry to cost-effectively meet new environmental requirements. Membranes, ion exchange resins and precipitation are feasible methods to treat effluents but these are normally constrained by high operating costs and/or conditions. In this context, solvent extraction appears as a powerful technique as it allows recycling of metal ions and water from both diluted and concentrated solutions (Andersson & Reinhardt, 1983).

Solvent extraction is a well-established separation method used in hydrometallurgical processing of several metals that consists basically of three main steps. In the extraction step, the metal-bearing aqueous feed solution (effluent) is contacted with an organic (or solvent) phase that contains an extractant agent dissolved in a diluent (normally commercial kerosene). The metal of interest reacts with the extractant and it is transferred from the aqueous to the organic phase. The liquid phases are then separated and the aqueous one is submitted for the recovery of other metals, to be recycled or even discharged, while the organic phase goes on to the next step. If selectivity in the extraction step is low, the loaded organic phase goes to the scrubbing step to remove other metals or impurities co-extracted using a suitable aqueous solution that may be recycled to a stage upstream of the circuit. Finally, in the stripping step, the metal in the loaded solvent is stripped out from the organic phase to some suitable aqueous solution resulting in a fairly concentrated solution on the metal of interest (as a metal salt form), which goes to further processing for pure metal or metal oxide production (electrolysis, evaporation, crystallization, etc). According to Ritcey and Ashbrook (1984), the solvent extraction is a simple operation requiring just a shift in the equilibrium between the extraction and stripping processes, so the selectivity of the extractant and its metal loading capacity represent decisive parameters to be defined in a separation process based on solvent extraction.

Nowadays, there is a large number of available stable extractants showing excellent selectivity characteristics coupled with advances in engineering and increasing demands for higher purity products and more environmentally friendly processing routes. In this context, the main technical aspects of three different applications are detailed as follows aiming to demonstrate the range of practical applicability of solvent extraction in the environmental field: (1) separation and concentration of Zn from effluents generated by the zinc industry (Pereira et al., 2007), (2) separation of Zn and Fe from pickling effluents produced by the hot-dip galvanizing industry (Mansur et al., 2008), and (3) recovery of base metals like Co and Ni from spent batteries (Mantuano et al., 2006; Dorella & Mansur, 2007). Such investigations at laboratory and/or pilot scales using batteries of mixer-settlers were carried out by our research team at UFMG in cooperation with industry (Votorantim Metais, ABB Ltda, etc.) and institute CDTN (Centro de Desenvolvimento da Tecnologia Nuclear). The main achievements are discussed as follows.

 

Case studies

Zinc recovery from zinc industrial effluents

A sulphuric acid effluent containing predominantly Zn and many other metals in lower concentrations ([Zn] = 13.5 g/L, [Co] = 0.7 mg/L, [Cd] = 22.7 mg/L, [Fe] = 240.6 mg/L, [Pb] = 5.4 mg/L, [Ca] = 0.6 g/L, [Mg] = 2.4 g/L, [Mn] = 0.75 g/L, pH = 3.1) was treated by solvent extraction with D2EHPA (di-2-ethylhexyl phosphoric acid) dissolved in Exxsol D-80 in order to selectively separate Zn and concentrate it. The effluent was produced by Votorantim Metais Co. (Brazil), which is the fifth largest zinc producer in the world today. The effluent is currently treated by precipitation with soda, resulting in a considerable amount of sludge containing several metals, while water is reused and/or discharged. The sludge is disposed in landfill and/or preferentially reused in the industrial plant to adjust the pH of aqueous streams. Both pathways have disadvantages: in the former, all metals are lost (environmental liability) while in the latter, Zn is recovered but remaining metals precipitated as metal hydroxides are reprocessed again and again, so they accumulate in the plant. In this context, the inclusion of a solvent extraction step with D2EHPA (di-2-ethylhexyl phosphoric acid) as extractant to treat the effluent could recover zinc (main species present in the effluent), separate it from the other metals that could be precipitated with NaOH and reuse water. The precipitation of the remaining metals will involve a considerable lower consumption of soda, so a smaller volume of sludge is generated for disposal, avoiding the return of such metals to the industrial process.

Bench scale tests revealed that D2EHPA extracts metals according to Zn >> Fe ~ Pb > Cd ~ Ca > Mg ~ Mn ~ Co. Based on their pH1/2 values, four separate metal groups were distinguished: Zn (pH1/2 ~ 0.9), Fe and Pb (pH1/2 ~ 2.0 - 2.2), Cd and Ca (pH1/2 ~ 2.9 - 3.2), and Mg, Mn and Co (pH1/2 ~ 4.3 - 4.8). Therefore, zinc can be separated ahead of all the other metals at low pH values. For pH = 1.5, Zn extraction increased from 35 to 80% when the concentration of D2EHPA was raised from 10 to 30%w/w while all Zn was extracted at D2EHPA concentrations higher than 25%w/w for pH = 2.5. At 20%w/w of D2EHPA, the extraction of Ca dropped from 30 to 14% while the extraction of Mg dropped from 20% to null, respectively. On the other hand, Fe extraction increased from 18 to 60% while Zn went from 65 to 95%. This result points out that Zn and Fe are preferably extracted by D2EHPA than Ca and Mg at higher pH values. The considerable reduction in Mg extraction at the expense of the increase of Fe extraction seems more convenient because (1) the concentration of Mg in the feed is comparatively higher so 60% of Fe extracted at pH 2.5 corresponds to 156.4 mg/L Fe in the extract while 21% of Mg extracted at pH 1.5 corresponds to 520 mg/L Mg in this phase (the same can be said for Ca), (2) for Votorantim Co., Zn and Mg must be preferentially separated in this step to reduce the amount of Mg in the industrial circuit, and (3) around 98% of Zn is extracted at pH = 2.5, so a lesser number of mixer-settlers will be required. The method was then found feasible to recover Zn from the effluent. As shown in Figure 1, Zn concentration and total concentration of the remaining metals in the effluent decreases as the A/O ratio reduces. It is interesting to notice that Zn concentration decreases with A/O ratio for the whole range studied, reaching a very low concentration (high Zn extraction) at A/O ratio ³ 1/2. On the other hand, the total concentration of remaining metals exhibits a quite constant value which is similar to those of feed at A/O ratios ³ 1, having a significant drop only at A/O ratios < 1. So, it seems to be advantageous to extract Zn at A/O = 1, pH 2.5 and 20%w/w of D2EHPA.

 

 

 

Pilot scale tests were then carried out using a mixer-settler cascade (3 extraction and 3 stripping stages) continuously operated in counter-current manner. In the extraction unit, both streams were fed at 12 mL/min (A/O = 1) and, in the stripping one, the stripping solution stream consisting of an industrial H2SO4 solution (nearly 2 M) was fed at 3 mL/min (O/A = 4). Results are summarized in Figure 2.

 

 

 

Almost all Zn was extracted in the extraction unit but Zn concentration in raffinate is still too high to discharge water, so it must be polished to remove all remaining metals to permit its safe disposal. The extraction of Fe and Mg was low, around 38.5% and 6.0%, respectively; in fact, the total concentration of remaining species did not change significantly. In the tripping unit, 98% of Zn was recovered from the extract thus resulting in a solution with 125.7 g/L of Zn that can be sent to electrowinning. The concentration of other metals in the stripping solution was quite unchanged.

Separation of zinc and iron from pickling effluents

The treatment of effluents generated by metal plating industry is normally carried out by precipitation with soda, NaOH, or lime, Ca(OH)2 (or a mixture of both). It is an efficient method to clean water from spent HCl pickling effluents but unfortunately both acid and metal content confined to the sludge are not reprocessed. The amount of precipitating agents required for treatment and the cost for the safe disposal of sludge are normally high, so solvent extraction can be an interesting alternative to separate Zn and Fe, and recycle the water. In HCl media, it has been found that Zn can be selectively separated from Fe(II) using TBP (tri-nbutyl phosphate), Cyanex 301 [bis(2,4,4- trimethylpentyl) dithiophosphinic acid] or Cyanex 272 [bis(2,4,4-trimethylpentyl) phosphinic acid] as extractants, so Fe(III) must be reduced to Fe(II) in a previous step otherwise the Zn/Fe selectivity factor decreases considerably. In order to show such characteristics, two effluents with distinct concentration levels were studied: effluent 1 (70.2 g/L of Zn, 92.2 g/L of Fe, acidity 0.25 M) was treated with TBP while effluent 2 (33.9 g/L of Zn, 230.91 g/L of Fe, acidity 2 M) was treated with Cyanex 272 and Cyanex 301. In all situations, zinc was extracted selectively while iron was left in the aqueous phase. Furthermore, zinc is extracted at low pH, so the cost to increase pH is minimal.

Figure 3 shows the extraction of Zn and Fe from effluent 1 with organic solutions containing 50%v/v of TBP (dissolved in Exxsol D-80) and 100%v/v of TBP at changing organic/aqueous volumetric ratio of phases. It can be observed that the efficiency of the Zn/Fe separation increases at higher TBP/aqueous solution volumetric ratio. For 50%v/v of TBP, the Zn/Fe selectivity factor increased from 4.4 to 16.0 as the O/A volumetric ratio was changed in the investigated range; for 100%v/v of TBP, it increased from 9.1 to 98.0.

The efficiency of extractants Cyanex 272 and Cyanex 301 for the extraction of Zn and Fe from effluent 2 is shown in Figure 4 at changing acidities (or pH) of the aqueous phase. Cyanex 301 was found to be significantly superior to Cyanex 272 to separate Zn and Fe and, for the operational conditions investigated, a maximum in the selectivity Zn/Fe (around 350) was found at pH=0.75 for Cyanex 301. At higher pH values (or lower acidities), the increase in the extraction of iron reduces the selectivity factor. Cyanex 301 can separate Zn over Fe(II) in a few stages but the stripping step will require very concentrated HCl solutions.

Recovery of base metals from spent betteries

Mobile phones, laptops, palmtops, digital cameras, and many other portable electronic devices are indispensable equipment today that require rechargeable batteries. For instance, the number of mobile phone subscribers in the world was estimated at 2.14 billion in 2005 and it grows everyday everywhere. In Brazil, there are more than 200 million mobile phones in operation nowadays. The higher the number of mobile phones or any other electronic device in use worldwide, the higher the number of spent batteries that must be recycled to avoid pollution. Such type of residue is an important secondary source of metals that can be normally found at very high concentration levels, sometimes even higher than those found in natural ores, so it must be recycled not only for environmental reasons. Some metals are expensive such as Co and Ni. According to our estimates, NiCd batteries typically contain (2.0±0.8)%w/w Co and (22±14)%w/w Ni, NiMH batteries contains (6.1±0.7)%w/w Co and (49±5)%w/w Ni and Li-ion batteries contain (36±9)%w/w Co, excluding the plastic and metallic shells. Therefore, recycling of spent batteries may result in economic benefits, so solvent extraction could be a useful method to produce pure metals or metal salts to be recycled from this kind of residue.

As most spent batteries contain Co and Ni as valuable metals to be recovered, Cyanex 272 naturally appears as a potential reagent to be used to separate metals present in this type of residue. As shown in Figure 5, it was found that metal extraction from sulphuric acid solutions with Cyanex 272 occurs according to the following pH sequence: Zn2+ > (Mn2+ = Co2+ = Cd2+) > Ni2+ > Li+. The pH1/2 values obtained are 2.5-3.0 for Zn, 4.0-4.5 for Mn, Co and Cd, 6.3 for Ni and 8.0 for Li. Taking into consideration the typical metal composition of commercial batteries, it can be conclude that batteries must be classified and leached by type. Therefore, different treatment routes depending on the type of battery must be considered. Alkaline batteries contain mainly zinc and manganese that could be easily separated with Cyanex 272 or D2EHPA (Nathsarma & Devi, 2006). For NiCd batteries, Cyanex 272 can easily separate Cd from Ni that are present in major proportion in this type of battery. For NiMH batteries, Co could be easily separated from Ni which remains in the aqueous solution but an additional previous extraction step using D2EHPA will be necessary to separate Cd and Co if NiCd and NiMH batteries are leached together (Souza et al., 2005). Finally, for the Li-ion batteries, Co and Li can be separated with Cyanex 272. A very few number of contact stages will be required to separate Co from Li as evidenced by the isotherm of cobalt with Cyanex 272 according to the McCabe- Thiele method (Dorella & Mansur, 2007). The stripping of Co from the loaded organic phase can achieve very concentrated aqueous solutions, i.e., around 63 g/L of Co, with 0.4 g/L of Al and practically no Li. Therefore, solvent extraction separates Co efficiently thus resulting in concentrated solutions that might be directly sent to electrowinning.

 

Final considerations

The results achieved in these studies show that solvent extraction is a very efficient method to recover metals from industrial effluents or from leach solutions from residues. Batch and pilot scale studies reveal that solvent extraction might contribute to save energy by eliminating the energy required to transport hazardous materials to waste sites, by reducing the energy required to produce and process the raw metals that were previously discarded in waste sludge, and also by reducing the energy required for replacement of the discharged wastewater.

 

Acknowledgements

Sincere thanks to Votorantim Metals Co., ABB Ltd. and CDTN for technical support, and also to CNPq, CAPES, FINEP and FAPEMIG for financial support.

 

References

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SOUZA, R. M. P., LEÃO, V. A., PINA, P. S. Remoção de metais pesados em resíduos sólidos: o caso das baterias de celular. REM - Revista Escola de Minas, v. 58, n. 4, p. 375-379, 2005.         [ Links ]

 

Artigo recebido em 13 de fevereiro de 2008.
Aprovado em 11 de outubro de 2010.