Keywords

Introduction

Nickel laterite ores represent, approximately, 60% of worlds nickel resources, but only 50% of the annual production of nickel comes from laterite sources [1]. Although the nickel can be found in sulfide deposits and processed by conventional methods of mineral processing , the laterite ore has become an additional source considering its increasing demand [2].

The evolution of laterite profile makes four different zones, which could contain nickel (ferricrete, limonites, transition and saprolite ). It makes markedly variations into leaching behavior and the choice of processing route employed is driven by technical, financial and environmental requirements [3]. In laterite ore nickel is finely disseminated into the iron oxides structures and magnesium silicates, instead of the presence of a specific nickel mineral [4,5,6]. This makes conventional mineral processing not applicable to increase the nickel grade into a concentrated fraction [7, 8]. Therefore, hydrometallurgical processing is the most indicated approach to this kind of ore because the mineral phases containing nickel need to be broken up to liberate the metal in leaching solution [9].

The study of atmospheric leaching has been encouraged instead of high-pressure acid leaching (HPAL) technology because it can be settled at low temperatures avoiding expensive HPAL autoclaves [10]. However, key issues related to kinetics parameters of nickel dissolution and subsequent steps of purification of liquor have to be addressed [11].

Recent studies about nickel leaching from laterite ores have revealed a strong dependence to mineralogy and chemistry association of nickel to mineral phases [12,13,14]. In this way, the source of laterite ore could influence on the leaching behavior.

The study of kinetics parameters of low-grade lateritic nickel ore is a challenge due to its complex mineralogy and the presence of many Ni and Co bearing minerals . The purposed mechanism of sulfuric atmospheric acid leaching may be splited in three equations: (1), (2) and (3) [15, 16]. These equations represent the proton attack to Ni/Co mineralized particles (asbolane, serpentines and goethite) and release of nickel and cobalt to a pregnant solution.

$$ (Ni_{0.3} Co_{0.1} Ca_{0.1} )MnO_{1.5} (OH)_{2} 0.6H_{2} O_{(l)} + H_{2} SO_{4(aq)} \to NiSO_{4(aq)} + CoSO_{{4\left( {aq} \right)}} + CaSO_{4(aq)} + MnSO_{4(aq)} + H_{2} O_{(l)} $$
(1)
$$ \left( {Mg,Ni} \right)_{2} Si_{2} O_{5} \left( {OH} \right)_{4(s)} + H_{2} SO_{4(aq)} \to MgSO_{4(aq)} + NiSO_{4(aq)} + SiO_{2(aq)} + H_{2} O_{(l)} $$
(2)
$$ \left( {Fe,Ni} \right)OOH_{(s)} + H_{2} SO_{4(aq)} \to NiSO_{4(aq)} + Fe_{2} \left( {SO_{4} } \right)_{3(aq)} + H_{2} O_{(l)} $$
(3)

Although there are three main nickel -cobalt bearing minerals , overall, the controlling mechanism of leaching depends also on minor host minerals such as nontronite and magnetite [11]. Several kinetic models and reaction mechanism have been developed to identify the slowest step of leaching process [17]. In general, leaching of laterite ores follows shrinking core models which assumes the reaction wave develops progressively towards the center of particles through a porous layer in the particle.

Three steps, (i) proton diffusion through the liquid film and the porous layer, (ii) chemical reaction on the particle/porous surface and (iii) diffusion of reaction products through the porous layer and to the liquid film may control the reaction. The Eqs. (4), (5) and (6) represent the kinetics models of those controlling steps.

$$ x\;=\;k_{VD} \cdot t $$
(4)
$$ 1 - 3\left( {1 - x} \right)^{{\frac{2}{3}}} + 2\left( {1 - x} \right)\;=\;k_{PL} \cdot t $$
(5)
$$ 1 - \left( {1 - x} \right)^{{\frac{1}{3}}}\;=\;k_{CR} \cdot t $$
(6)

where x is the fraction leached or dissolved metal, k is the apparent rate constant and t is time.

Equation 4 assumes that the controlling step is the volume diffusion (VD), Eq. 5 assumes control is due to diffusion in ash porous layer (PL) and Eq. 6 undertakes chemical reaction (CR) as the slowest step of process and controls the leaching .

Determination of activation energy (Ea) for the reaction through Arrhenius correlation between apparent rate constant and absolute temperature (T) as show in the Eq. 7 helps in identifying the controlling step. In this equation R is the ideal gas constant and k0 is the pre-exponential factor. Ea is generally low for diffusion-controlled process (<20 kJ mol−1) while to chemical reaction control the activation energy is higher (>40 kJ mol−1)

$$ k = k_{0} \cdot e^{{ - \frac{{E_{a} }}{RT}}} $$
(7)

Many authors have been studying the kinetics and the parameters associated to the dissolution time of nickel from laterite ores [4, 12, 13, 18,19,20,21]. However, the determination of reaction order with respect to nickel can be quite complex since there are multiples sources of nickel in the ore , as pointed out by [15, 16].

Kinetics studies of nickel leaching from laterite ores revealed a strong dependence on temperature which is mainly associated to chemical reaction control [4, 12, 13, 18]. However, other studies found a process control by diffusion into porous layer [18]. These authors found diffusion through porous layer was the controlling step to nickel extraction in any conditions of particle size and solid pulp densities. Nevertheless, cobalt diffusion into porous layer controlled the process at lower temperature (25 °C), but chemical reaction was determinant at higher temperature (90 °C). This inversion in the controlling steps suggests that a mixed process occurs, changing as function of temperature .

Control by mass transfer (diffusion) at lower temperature for chemical reaction is reported in literature [13, 22]. There is a correlation of temperature with the kinetics equation (Arrhenius equation) and in the diffusion coefficient [23]. These equations show different relation to temperature . While the Arrhenius equation depends on inverse exponential temperature , the diffusion coefficient is linearly dependent on temperature , which implies in more significant terms at higher temperatures for chemical reaction control .

Evaluation of the controlling steps of Ni leaching applying the Eqs. 4, 5 and 6 was carried out by MacCarthy et al. [12]. They indicated that only one controlling step was not enough to explain the kinetics observed. They divided the leaching time into two parts: one comprising the initial 30 min of reaction and the second one the last 210 min. They found 40% of nickel extraction in the first minutes, level that reached 80% at the end of leaching time for particle size of −0.200 mm, 95 °C and pH 1.

The kinetics model split in two parts (until 30 min and from 30 to 240 min) shown better adjustment to the data. This division was applied, according to the authors, because there is mineral phases such as smectite (Mg-silicates) of easier dissolution, which occurs in the first minutes while the nickel associated to refractories minerals needs more time to be released from their structure [4, 12]. Although the study of kinetics was separated in two distinct period of time, the chemical reaction control was found for both.

Applying a detailed evaluation for Chinese lateritic ore , the authors concluded that the shrinking core model fitted the results, but in different moments there is a distinct step that controls the reaction [13]. In the first minutes, which are different for distinct temperatures analyzed, the control is chemical while the diffusion control was observed after 50 min of leaching . According to the authors, better kinetics parameter was found at 270 °C at which the resistance to diffusion is low.

In this paper the kinetics and the controlling steps of process for a Brazilian nickel laterite ore is evaluated. The sample was also characterized in order to identify the mineral phases and nickel bearing minerals , and the controlling step of leaching was evaluated through classical shrinking core model .

Materials and Methods

Sample and Characterizing

Laterite ore from Brazil was received in sets of 5 kg from the mining. It was sieved and dried at 60 °C for 24 h. After homogenization and sampling, samples were kept to physical, chemical and mineralogical characterization . Particle size distribution , X-ray diffractometer (XRD) , scanning electron microscopy with chemical analysis (SEM /EDS ) and atomic adsorption spectrometry (AAS) were applied to identify and quantify mineralogical phases and their association to nickel or to the particle size fractions. Fe, Mg, Mn and Co was also analysed besides nickel . After ore characterization fractions were prepared to leaching study.

Leaching and Kinetic Evaluation

The experiments were carried out in a 1 L glass reactor equipped with Teflon impeller (400 rpm) and electrical heater, controlled by a thermostat (±0.1 °C). Leaching temperatures were set at 65 °C and 95 °C and ore fraction was added (−0.500 + 0.150 mm, −0.150 + 0.075 mm or −0.075 mm) to obtain a pulp density of 20%. Experiments with 0.9 mol L−1 sulfuric acid solution were developed to determine the mechanism control of leaching and the activation energy for Ni, Fe and Mg reactions. Samples were collected at 15, 30, 60, 120, 180, 240 min of leaching , vacuum filtered in filter paper with porosity of 8 μm, followed by filtration in fiberglass with porosity of 1 µm. Ni, Fe and Mg contents in liquor were quantified by atomic absorption spectrometry (AAS). Leaching control and the activation energy were evaluated trough the shrinking core model .

Results and Discussion

Sample Characterization

The particle size distribution of the ore shows that particles bellow 0.075 mm represent more than 50% of the ore and 44% of particles are smaller than 0.038 mm. Also, more than 20% are very tiny particles (below 0.010 mm), as expected for laterite ores, which contributes to suggest a transition to limonitic ore . These results are in good agreement with those reported by the literature [4, 5, 20, 24]. The characterization of particles including chemical and granulometry suggests a size-fractionating in −0.500 + 0.150 mm, −0.150 + 0.075 mm and −0.075 mm.

Quartz , chlorite, hematite, goethite and magnetite/maghemite were identified as major phases in this ore sample. This is also in a good agreement with nickel laterite ores from Indonesia, Iran, Australia, New Caledonia, China and Turkey [5, 25,26,27,28]. Some other mineral phases such as lizardite and chromite were detected too, but in small amounts.

Quantitative analysis, by Rietveld method, shows a concentration of Mg-minerals predominates in the coarser fraction (−0.500 + 0.150 mm) with 28% as lizardite and chlorite. The iron oxide phases, on the other hand, are concentrated in fine fraction (−0.075 mm) reaching up 56% with goethite being the main mineral corresponding to 42% of the fraction. In the full ore , Mg-minerals represent 25% with chlorite as major phase (21%), and iron oxide phases respond for 39% and being goethite 28% of sample. The −0.150 + 0.075 mm is a transitional fraction between −0.500 + 0.150 mm and −0.075 mm.

Ni is associated with oxides and silicates phases (Fig. 1) and as it was expected to this kind of ore, one specific mineral phase of nickel was not found, that was already indicated by the XRD analysis. The Ni contained in these deposits is mainly associated to specific mineral or it is closely associated to goethite by substitution of Fe in the crystalline structure [6, 29, 30], or it is incorporated into the magnesium silicates, explained by the aggressive weathering underwent by the rock [31].

Fig. 1
figure 1

Back scattered electron images and energy dispersive X-ray spectroscopy analysis of Ni-bearing silicate (a) chlorite (b) and iron oxide (c)

According to quantitative chemical analysis presented in Table 1, Ni and Fe are concentrated in the ore fraction below 0.075 mm while Si shows another trend, being concentrated in the coarser fractions, above 0.075 mm. Additionally, the chemical analysis confirms iron oxide concentrates in the fine fraction and it is also indicated that silicates are mostly in the coarser particles. Co and Mn do not show any accumulation profile in a specific range of particle size. Although Mg does not present concentration in any fraction, quantitative XRD analysis indicated that Mg-minerals (chlorite and lizardite) are concentrated in the coarser fraction.

Table 1 Quantitative chemical analysis (%) of Brazilian laterite nickel ore

Through this characterization and other summarized from the same ore , the total ore was fractionated in three samples with specific particle size range to evaluated the behavior in the leaching process and to access the kinetics study [32].

Leaching Experiments and Leaching Process Step Control

Figure 2 presents nickel , iron and manganese extractions along leaching time. Elements extractions show different behaviors for distinct temperatures. Intermediate fraction (−0.150 + 0.075 mm) presents a transitional behavior since at lower temperature the extraction curve is like fraction −0.075 mm while at higher temperature it is similar to the coarser fraction (−0.500 + 0.150 mm). It can be clearly observed that at 65 °C nickel extraction is similar for fractions −0.150 + 0.075 mm and −0.075 mm, however higher extractions were obtained for the coarser fraction.

Fig. 2
figure 2

Nickel, Iron and Magnesium extraction and its correspond correlation coefficient adjustment of the model best fit data, porous layer diffusion, for −0.500 + 0.150 mm, −0150 + 0.075 mm and −0.075 mm at 65 and 95 °C, solid-liquid ratio of 20%, initial sulphuric acid concentration 0.9 mol L−1 and stirring rate of 400 rpm

Although nickel extractions were very distinct to each size fraction, concentrations in the liquor were approximately equal for all of them. It reaches 1525 mg L−1 (−0.500 + 0.15 mm), 1023 mg L−1 (−0.150 + 0.075 mm) and 1222 mg L−1 (−0.075 mm) at 65 °C and 1672 mg L−1 (−0.500 + 0.15 mm), 1923 mg L−1 (−0.150 + 0.075 mm) and 1710 mg L−1 (−0.075 mm) at 95 °C. This comes from the difference between the Ni grades in distinct fractions and also due to mineralogy association of nickel and gangue minerals . Iron extraction average for three fractions raised from 6.5% (65 °C) to 11% (95 °C) being the concentration in the final liquor between 3811 and 6000 mg L−1 (65 °C) and 5896 and 9000 mg L−1 (95 °C). Therefore, extraction of Mg reached high level with concentrations of 6118 mg L−1 and 7750 mg L−1 (−0.500 + 0.150 mm at 65 and 95 °C). So, this behavior indicates that nickel in the fine fraction is major associated to iron oxide and in the coarser fraction with the silicates.

The kinetics analysis was completed applying the shrinking core model (Eqs. 4, 5 and 6) to three different size fractions and temperatures (Fig. 2 and Table 2).

Table 2 Apparent kinetic constant from better fit of shrinking core model and correlation coefficient (R2) for leaching experiments at 95 °C, 0.9 mol L−1 20% solid-liquid ratio and 400 rpm

At 95 °C, a single control for the whole period is not consistent with the data since there is a strong change in the slope of the linearized curve between 0 to 60 min and 60 to 240 min. It is verified that for 0 to 60 min process is controlled by diffusion into the porous layer, substantiated by the lower value of the kinetic constants and a better correlation coefficients (R2) than obtained for volume diffusion and chemical reaction controlling mechanisms. From 60 to 240 min, the porous layer diffusion and chemical reaction models present similar adjustments (R2) as well as the same order of apparent kinetic constants. Although some adjustments had low correlation coefficients (less than 0.90), the apparent velocity constants are lower in all fittings for the −0.075 mm fraction, corroborating that this fraction limits the process. Table 3 shows the activation energies determined for Ni, Fe and Mg using the regression of the porous layer step as the process control for the period between 0–60 min.

Table 3 Apparent velocity constant and activation energy for the shrinking core model with porous layer diffusion control for experiments at initial acid concentration of 0.9 mol L−1, 20% of solid-liquid ratio and stirring rate of 400 rpm 1 for the period between 0–60 min

The control by diffusion in porous layer was not expected, since several authors obtained the chemical reaction as a controlling step [4, 12, 13]. However, the widespread distribution of nickel in this ore may be the reason of this fact since nickel is disseminated into the mineral matrix and leaching greatly depend on reagents/products diffusion into the pores.

Conclusions

Leaching of Brazilian nickel laterite ore under atmospheric acid leaching has shown a mixed control depending on temperature . The ore , mainly composed by Mg-silicates and Fe-oxides, contains Ni widespread into the mineral matrix, which affected the kinetic of leaching, in distinct way for different size fractions. In the fraction with sizes below 0.075 mm, 2.07% of Ni is associated to iron oxides while in the coarser fraction, Ni is associate to magnesium silicates. This difference in mineralogy associated to particle sizes affected the kinetic of leaching . For this particular ore , leaching is controlled by porous layer diffusion independently on particle size at 65 °C, however a mixed control is present at 95 °C. Therefore, activation energy is in order of chemical reaction mechanism for leaching process.