metals
Article Extraction of Iron and Manganese from Pyrolusite Absorption Residue by Ammonium Sulphate Roasting–Leaching Process
Lin Deng, Bing Qu, Shi-Jun Su, Sang-Lan Ding and Wei-Yi Sun *
College of Architecture and Environment, Sichuan University, Chengdu 610065, China; [email protected] (L.D.); [email protected] (B.Q.); [email protected] (S.-J.S.); [email protected] (S.-L.D.) * Correspondence: [email protected]; Tel.: +86-028-8564-7252
Received: 21 December 2017; Accepted: 5 January 2018; Published: 8 January 2018
Abstract: The residue from desulfurization and denitrification of exhaust gas treatment process with pyrolusite ore as absorbent is regarded as a potential source of iron and manganese. In this study, an extraction process is proposed for recovery of iron and manganese with ammonium sulphate roasting followed by sulphuric acid leaching. Firstly, the conversion mechanism was analyzed through mineral phase analysis of roasting products at different roasting temperature by means of X-ray diffraction (XRD) technology. Then, the parameters of the roasting procedure such as roasting temperature and time, ammonium sulphate dosage, leaching temperature, leaching time, and sulphuric acid concentration are examined. The results implicate that the iron oxide and
manganese dioxide in the residue are firstly converted into the water-soluble (NH4)3Fe(SO4)3 and ◦ (NH4)2Mn2(SO4)3 at 200–350 C, and then the more stable NH4Fe(SO4)2 and MnSO4 are formed, at temperature higher than 350 ◦C. Under optimum conditions, 95.2% Fe and 97.0% Mn can be extracted. Reactant diffusion through inert layer of silicon dioxide was considered as the rate-limiting step for iron extraction with an activation energy of 20.56 kJ/mol, while, the recovery process of Mn was controlled by both reactant diffusion and chemical reaction with an activation energy of 29.52 kJ/mol.
Keywords: pyrolusite absorption residue; recovery; iron; manganese; ammonium sulphate; roasting
1. Introduction
SO2 and NOx emission from combustion of coal, fuel oils and waste have brought significantly important effects on environment and human health. Various kinds of technologies [1,2] have been developed to control and reduce SO2 and NOx emissions worldwide. Among these methods, pyrolusite ore adsorption has been regarded as one of the most promising technologies [2,3]. This is because it can successfully combine the removal of pollutants from flue gas, together with the manganese extraction from poor-grade pyrolusite ore [2,4]. Pyrolusite is a manganese oxide ore with manganese dioxide as its main component [5], which can oxidize the SO2 and NO, NO2 in the 2− − exhaust gas into SO4 and NO3 , respectively. These reactions can be written as the following:
2+ 2− MnO2(s) + SO2 = Mn + SO4 (1)
+ 2+ − 3MnO2 + 2NO + 4H = 3Mn + 2NO3 + 2H2O (2) 2+ − MnO2(s) + 2NO2 = Mn + 2NO3 (3)
Our previous studies [2,3] implicated that the removal efficiency of SO2 and NOx reached about 90% and 82% respectively, and the extraction efficiency of manganese can be maintained
Metals 2018, 8, 38; doi:10.3390/met8010038 www.mdpi.com/journal/metals Metals 2018, 8, 38 2 of 12 at 80~86%, with a pulp density of 500 g/L and a leaching temperature of 25 ◦C. The recovery products
(MnSO4 and Mn(NO3)2) meeting the national standard (HG/T 3817-2006) can be obtained through the further treatment of the absorption liquid, such as the removal of iron and heavy metal ions [6]. Unavoidably, the pyrolusite absorption residue (PAR) was produced in the process of desulfurization and denitrification using pyrolusite ore. The PAR is featured by high iron content, silicon dioxide and remaining manganese dioxide, and it also contains some heavy metal ions, such as cobalt, nickel, barium and calcium ions [7]. However, there are limited investigations on how to deal with these residues in order to reduce the risks of polluting environment. The PAR used to be an adsorbent for the treatment of Congo red and dyeing waste water, and satisfying removal efficiency were reported [8–10]. Lang et al. [11] pointed out that after adding limestone and bauxite, the residue can be used to generate sulphoaluminate cement. On the other hand, more than 45% iron oxide and 4% manganese dioxide were enriched in the PAR, which also can be regarded as a secondary source for iron and manganese. In the past few decades, many methods have been developed to recover iron and manganese from various mineral [12], wastes [13] and residues [14,15]. The reduction roasting-magnetic separation is widely used for iron recovery from red mud using coal [16], sodium carbonate [14] and pyrite [17] as reducing agent at 600–1300 ◦C and the iron recovery efficiency is generally over 85%. Oxalate also was adopted for iron leaching with the advantages of fast leaching rate, high extraction efficiency, attributing its higher chelate ability [18,19]. Manganese recovery can be realized from low-grade ◦ ◦ pyrolusite ore by roasting, using elemental sulphur at 350–500 C[20] or SO2 at 500 C[21] followed by sulphuric acid or water leaching; also by hydrometallurgical treatment processes including aqueous SO2 [15,22], FeSO4 [23], and biomass [24] However, these methods do not meet the requirements for the simultaneous recovery of iron and manganese. Rolf R.F [25] presented their work that 97% manganese and 47% iron can be extracted at the same time by firstly reducing with gaseous hydrogen, carbon monoxide or mixtures at 550~800 ◦C a then leached with ammonium sulphate solutions. Although the high recovery efficiency of both Mn and Fe were obtained, this process consumes more energy and used hazardous gases (H2, CO) as reducing gases. Recently, our group has found that ammonium sulphate, a widely available, low-cost, recyclable chemical agent can be used for extracting various metals containing Co, Ni, Mn and Al from low-grade nickel ore [26], zinc leaching residues [27], mine residues [28] and coal fly ash [29]. The extraction efficiency of manganese from the above minerals can achieve satisfying results i.e., higher than 80%. However, the iron leaching rate is lower, generally less than 50%. It is surprising that the iron recovery efficiency from ilmenite ore [30] and high-iron bauxite ore [31] could yield higher than 85%. The discrepancy of iron leaching efficiency obtained among these literatures [13,26,29–31] may be attributed to the different purpose of metal recovery; iron was generally regarded as impurities in these reports so that it was restricted to be extracted out. However, research aimed at simultaneous recovery of iron and manganese from minerals or other waste residue using ammonium sulfate as extracting agent has not been reported in literatures. In this paper, the feasibility of sulphating roasting of PAR with ammonium sulphate was comprehensively investigated. The role that ammonium sulphate plays in the sulphating roasting process and corresponding reaction mechanism are discussed. The roasting kinetics were analysed to elucidate the extraction characteristics of manganese and iron. The effect of ammonium sulphate-to-PAR ratio, roasting temperature, roasting time, leaching temperature, leaching time, and sulphuric acid concentration on the extraction behavior have been studied.
2. Materials and Methods
2.1. Materials The Pyrolusite Absorption Residue (PAR) was generated during the flue gas desulfurization process using iron-rich pyrolusite ore as desulfurizer. The obtained residue was washed with distilled water and milled to a size of 200 mesh after dried at 80 ◦C for 3 h prior to experiments. The chemical Metals 2018, 8, 38 3 of 12 Metals 2018, 8, 38 3 of 12 distilledcomposition water of and this milled residue to is a shown size of in 200 Table mesh1. The after average dried at iron 80 and°C for manganese 3 h prior contentsto experiments. were 30.1% The chemicaland 4.03%, composition respectively. of this The residue main minerals, is shown whichin Table are 1. evidentThe average from iron the X-rayand manganese diffraction contents pattern were 30.1% and 4.03%, respectively. The main minerals, which are evident from the X-ray diffraction (Figure1), are goethite (FeOOH) and silicon dioxide (SiO 2). The analysis grade ammonium sulphate pattern (Figure 1), are goethite (FeOOH) and silicon dioxide (SiO2). The analysis grade ammonium ((NH4)2SO4) was used in all experiments. sulphate ( NH ) SO ) was used in all experiments. Table 1. Chemical composition (metal content) of the pyrolusite absorption residue (PAR) used Tablefor experiments. 1. Chemical composition (metal content) of the pyrolusite absorption residue (PAR) used for experiments.
ElementsElements Fe FeMn Mn Al Al Ca Ca Ba Ba Zn Zn Ni Ni Cu Cu Content Content(wt. %) (wt. %) 30.1 30.1 4.03 4.03 1.75 1.75 0.761 0.761 0.491 0.491 0.044 0.044 0.029 0.029 0.021 0.021
Figure 1. 1. TheThe X-ray X-ray diffraction diffraction of ofpattern pattern of of(a) (thea) thePAR; PAR; (b) (theb) theleaching leaching residue residue after after roasting-acid roasting- leaching.acid leaching.
2.2. Methods and Procedure 2.2. Methods and Procedure Roasting experiments were conducted in a fixed horizontal electric tube furnace (SK-G04123K Roasting experiments were conducted in a fixed horizontal electric tube furnace (SK-G04123K Tianjin Zhonghuan Lab Furnace Co., Ltd., Tianjin, China). The experimental apparatus is presented Tianjin Zhonghuan Lab Furnace Co., Ltd., Tianjin, China). The experimental apparatus is presented in in Figure S1. As the tube is heated the required temperature at a rate of 10 °C /min, then a Figure S1. As the tube is heated the required temperature at a rate of 10 ◦C /min, then a corundum corundum crucible loading mixture of PAR and ammonium sulphate was sent into the roasting crucible loading mixture of PAR and ammonium sulphate was sent into the roasting zone. At the end zone. At the end of the tube, the exhaust gas (NH3) was collected by NaOH solution. After each of the tube, the exhaust gas (NH3) was collected by NaOH solution. After each roasting experiment, roasting experiment, the roasted PAR was leached by water and diluted sulphuric acid to transfer the roasted PAR was leached by water and diluted sulphuric acid to transfer soluble sulphate salt soluble sulphate salt into solution. The leaching slurry was filtered with 0.45 μm membrane, and the into solution. The leaching slurry was filtered with 0.45 µm membrane, and the filtrate and residue filtrate and residue then were separated. The leaching liquid was collected to determine the recovery then were separated. The leaching liquid was collected to determine the recovery percentage of percentage of manganese and iron. The influence of different parameters including: ammonium manganese and iron. The influence of different parameters including: ammonium sulphate dosage, sulphate dosage, roasting temperature, and roasting time, as well as leaching temperature, time, and roasting temperature, and roasting time, as well as leaching temperature, time, and leaching acidity leaching acidity were studied in the way that one parameter was tested while keeping other were studied in the way that one parameter was tested while keeping other parameters constant. parameters constant. 2.3. Product Analysis 2.3. Product Analysis Spectrophotometry was employed for Fe analysis using MAPADA V-1200 VIS spectrophotometer. ManganeseSpectrophotometry was determined was by employed ICP-MS (NEXION for Fe 300X,analysis PERKINELMER, using MAPADA San Diego, V-1200 MA, USA)VIS spectrophotometer.equipped with an autoManganese sampler was (SC2 determined DX, ESI, PERKINELMER,by ICP-MS (NEXION San Diego,300X, PERKINELMER, MA, USA). A X-ray San Diego,diffraction MA, (XRD)USA) equipped equipment with (EMPYREAN, an auto sample PANalytical,r (SC2 DX, Almelo, ESI, PERKINELMER, The Netherlands) San wasDiego, used MA, to USA).identify A theX-ray solid diffraction components (XRD) of theequipment PAR and (EMPYREAN, roasting products. PANalytical, Almelo, The Netherlands) was used to identify the solid components of the PAR and roasting products.
Metals 2018, 8, 38 4 of 12
3. Results and Discussion
3.1. Reaction Mechanisms
3.1.1. Reaction between PAR and Ammonium Sulphate In order to understand the roasting process of thermochemical treatment of the absorption residue (PAR) with ammonium sulphate, it is important to gain insight in the thermal decomposition of pure
(NH4)2SO4 over the temperature range studied, since it will affect greatly the thermochemical process. The published literatures revealed disagreement as to the nature of the intermediate species formed during thermal decomposition of ammonium sulphate. Nevertheless, a general consensus [30,32–34] is that the decomposition mechanism may involve the following steps:
>100 ◦C (NH4)2SO4−−−−→ NH4HSO4(s) + NH3(g) (4)
100−170 ◦C (NH4)2SO4 + NH4HSO4−−−−−−→ (NH4)3H(SO4)2 (5) 170 ◦C NH4HSO4−−−→ NH2HSO3(s) + H2O(g) (6)
200 ◦C 3NH2HSO3(s)−−−→ NH3(g) + 3SO2(g) + N2(g) + 3H2O(g) (7)
170 ◦C NH4HSO4 + NH2HSO3−−−→ (NH4)2S2O7 (8) 400 ◦C (NH4)3H(SO4)2−−−→ (NH4)2S2O7 + NH3 + H2O (9) 400 ◦C 3(NH4)2S2O7−−−→ 2NH3 + 6SO2 + 9H2O + 2N2 (10) 400 ◦C 3(NH4)2SO4−−−→4NH3 + 3SO2 + 6H2O + N2 (11) KiyouraandUrano [33] confirmed the thermal decomposition of ammonium sulphate to ammonium bisulphate (Equation (4)) at temperature higher than 100 ◦C through release of ammonia, however, that is not being detected by X-ray diffraction method. This is because of the rapid reaction between ammonium sulphate and ammonium bisulphate to form triammonium hydrogen sulphate ◦ ((NH4)3H(SO4)2) (Equation (5)). Meantime, sulphamic acid is formed by release of H2O at 170 C (Equation (6)), which would further decompose into various gases including NH3, SO2,N2, and H2O (Equation (7)) [33]. Dixo [32] pointed out that the ammonium pyrosulphate ((NH4)2S2O7) from the reactions (Equations (8) and (9)) accounts for 90% of the products of ammonium sulphate during the thermal decomposition at 400 ◦C. But this is not consistent with the results in this article, where only triammonium hydrogen sulphate was detected by XRD. This may due to the formation of NH4HSO4 from the dehydration of (NH4)2S2O7. Studies [26,27,33] on the sulfation of iron oxides and MnO2 by ammonium sulphate at ◦ 300~500 C, have shown the major products to be (NH4)3Fe(SO4)3, NH4Fe(SO4)2, Fe2(SO4)3, Fe2O3, and (NH4)2Mn2(SO4)3, and MnSO4. Based on these reaction products, the chemical reactions taking place during the thermochemical treatment PAR in air atmosphere may be considered as follows:
FeOOH + 3(NH4)2SO4 → (NH4)3Fe(SO4)3 + 3NH3 + 2H2O (12)
FeOOH + 2(NH4)3Fe(SO4)3 → 3NH4Fe(SO4)2 + 3NH3 + 2H2O (13)
2NH4Fe(SO4)2 → Fe2(SO4)3 + 2NH3 + SO3 + H2O (14)
Fe2(SO4)3 → Fe2O3 + 3SO3 (15)
(NH4)2SO4 + 2MnO2 + 2SO2 → (NH4)2Mn2(SO4)3(s) (16)
(NH4)2Mn2(SO4)3(s) → 2MnSO4 + 2NH3 + SO3 + H2O (17) MetalsMetals 20182018, 8,, 838, 38 5 5of of 12 12
MnO SO →MnSO (18) MnO2 + SO2 → MnSO4 (18)
3.1.2.3.1.2. Characterization Characterization of of Roasting Roasting Product Product TheThe roasting roasting products products of of pyrolusite pyrolusite absorpti absorptionon residue residue (PAR) (PAR) with with ammonium ammonium sulphate sulphate at at temperaturetemperature of of 300–600 300–600 °C◦ Cwere were analyzed analyzed by byXRD XRD to study to study the theroasting roasting mechanism. mechanism. The results The results are presentedare presented in Figure in Figure 2. 2.
FigureFigure 2. 2. X-rayX-ray patterns patterns of of the the roasting roasting pr productsoducts at at different different temperatures. temperatures.
ComparedCompared with with the XRDXRD patternpattern of of the the residue residue (Figure (Figure1), the 1), XRDthe XRD diagram diagram of the productof the product roasted roastedat 300 ◦atC, 300 shown °C, inshown Figure in2, Figure indicates 2, thatindicates some that new some diffraction new diffraction peaks appeared peaks after appeared calcination, after calcination,but the change but the of the change mineral of the phase mineral was not phas obviouse was atnot 300 obvious◦C. With at 300 respect °C. toWith the respect analysis to result, the analysis result, the new materials are mainly NH ) Fe SO ) , and the peaks are weak and the new materials are mainly (NH4)3Fe(SO4)3, and the peaks are weak and unobvious (Equation (12)). unobvious (Equation (12)). In disagreement with line 1, the peaks of new products NH ) Fe SO ) In disagreement with line 1, the peaks of new products (NH4)3Fe(SO4)3 were more obvious than before werewith more increasing obvious roasting than temperature,before with increasing indicating ro thatasting more temperature, iron oxide was indicating sulphated. that Atmore the sameiron oxidetime, was the hematitesulphated. peak At wasthe alsosame observed, time, the suggesting hematite peak that the was goethite also observed, in the PAR suggesting was dehydrated that the at goethite350 ◦C toin formthe PAR a more was stable dehydrated hematite at (Equation350 °C to form (19)). a more stable hematite (Equation (19)).
2FeOOH s) → Fe O s) H O g) (19) 2FeOOH(s) → Fe2O3(s) + H2O(g) (19) As the calcination temperature continues to increase to 400 °C, the NH ) Fe SO ) diffraction ◦ peak formedAs the calcinationon lines 1–2 temperature disappears, continuesand a new to peak increase is formed to 400 in C,line the 3.( ThisNH4 peak)3Fe( SOis considered4)3 diffraction as NHpeak Fe formedSO ) , which on lines is1–2 a more disappears, stable andferric a newsulphate peak ammonium is formed in salt line formed 3. This from peak isthe considered reaction ) ) betweenas NH4 FeNH(SO 4 )Fe2, whichSO isand a moreFeOOH stable (Equation ferric sulphate(13)). When ammonium the roasting salt temperature formed from is the increased reaction ) upbetween to 450 (°C,NH more4)3Fe (NHSO4 )Fe3 andSO FeOOH was produced,(Equation (13)).because When both the the roasting correspondent temperature diffraction is increased peak up ◦ NH ) H SO ) andto 450intensityC, more increase.NH4Fe And(SO 4the)2 was diffraction produced, peaks because of both the correspondent have disappeared, diffraction indicating peak and thatintensity it has increase. been decomposed And the diffraction completely peaks at 500 of ( NH°C, 4and)3H (theSO4 )peak2 have of disappeared,ferric sulphate indicating is observed, that it indicatinghas been decomposedthe occurrence completely of Equation at 500 (14).◦C, When and the the peak roasting of ferric temperature sulphateis continues observed, to indicating increase theto ◦ 600occurrence °C, the peak of Equation of Fe O (14). can When be detected, the roasting which temperature indicates that continues some of to the increase ferric to sulfate 600 C, occurs the peak to decompose.of Fe2O3 can be detected, which indicates that some of the ferric sulfate occurs to decompose. OweOwe to to the the low low manganese manganese content content in inthe the PAR, PAR, it is it difficult is difficult to examine to examine the thephase phase conversion conversion of manganeseof manganese dioxide dioxide during during the theroasting roasting process process by byX-ray X-ray diffraction diffraction (XRD) (XRD) technology. technology. However, However, thethe roasting roasting mechanism mechanism of of manganese manganese dioxide dioxide wi withth ammonium ammonium sulphate sulphate can can be be analyzed analyzed on on the the basisbasis of of the the extraction extraction data data from from Figure Figure 3b.3b. It can be seen from Figure 33bb thatthat 56.4%56.4% MnMn waswas extracted at roasting temperature of 300 °C and roasting time of 240 min, which implicated that the
Metals 2018, 8, 38 6 of 12 manganese dioxide has been reduced into the water-soluble Mn . The following paper [27,30] examine the decomposition gas of ammonium sulphate, and the results show that the NH3 is the main gas when the temperature is below 380 °C, while, SO2 and H2O were mainly generated at 520 °C. Therefore, the sulfation-roasting process of manganese dioxide at lower temperature can be described through Equation (13). And this small amount of SO2 gas in Equation (16) was produced from the decomposition of sulphamic acid (NH HSO ) (Equation (7)). At a higher temperature, more SO2 was generated by Equation (11), which can directly react with manganese dioxide and form Metals 2018, 8, 38 6 of 12 manganese sulphate (Equation (18)) [21].
3.2.extracted Roasting at Kinetics roasting temperature of 300 ◦C and roasting time of 240 min, which implicated that the manganese dioxide has been reduced into the water-soluble Mn2+. The following paper [27,30] The roasting kinetics of PAR with ammonium sulphate was studied by water leaching in the examine the decomposition gas of ammonium sulphate, and the results show that the NH is the main temperature range of 275–400 °C. Other conditions were: 12 of ammonium sulphate-to-PAR3 ratio, gas when the temperature is below 380 ◦C, while, SO and H O were mainly generated at 520 ◦C. 60 °C of leaching temperature, and 120 min of leaching 2time. The2 effects of roasting temperature and Therefore, the sulfation-roasting process of manganese dioxide at lower temperature can be described time on manganese and iron extraction are shown in Figure 2a. With increasing roasting through Equation (13). And this small amount of SO gas in Equation (16) was produced from the temperature, the proportion of manganese and iron leached2 from the PAR increase. As for the iron decomposition of sulphamic acid (NH HSO ) (Equation (7)). At a higher temperature, more SO was roasting process, the extracted amount2 increased3 linearly at a roasting temperature of 2752 °C. generated by Equation (11), which can directly react with manganese dioxide and form manganese However, the maximum efficiency of Fe extracted was reached at roasting temperature of 300– sulphate (Equation (18)) [21]. 375 °C, within the roasting time studied.
Figure 3. The effect of roasting temperature on (a) iron and (b) manganese with sulphating Figure 3. The effect of roasting temperature on (a) iron and (b) manganese with sulphating roasting- roasting-water leaching. water leaching.
Increasing the roasting temperature has little effect on further increasing the extraction 3.2. Roasting Kinetics efficiency of iron. Table S1 shows the iron extraction from various minerals, such as mine tailings [28], Thenickel roasting laterite kinetics [26,35] ofand PAR ilmenite with ammonium [30], using sulphateammonium was sulfate studied as bya roasting water leaching agent. These in the ◦ resultstemperature implicate range that of the 275–400 iron extrC.action Other efficiency conditions is were: either 12 lower of ammonium or higher. sulphate-to-PARThis situation may ratio, be ◦ related60 C of to leaching the content temperature, of silica andin the 120 ore, min whic of leachingh may retard time. The the effectsdiffusion of roasting of ammonium temperature sulphate and throughtime on manganesethe ash layer and from iron the extraction surface to are the shown center in of Figure the PAR.2a. With When increasing the silica roasting is high, temperature,the recovery ratethe proportionof iron is low of manganese [26,28,35], and and iron vice leached versa the from recovery the PAR rate increase. of iron As is for high the ironwhen roasting the content process, of ◦ siliconthe extracted is low amount[30,31]. increasedAbout 95.6% linearly Fe can at a be roasting extracted temperature from the ofroasting 275 C. product However, of thepure maximum FeOOH ◦ underefficiency the ofsame Fe extractedconditions, was which reached further at roasting verify temperaturethe above-mentioned of 300–375 mechanismC, within that the the roasting iron roastingtime studied. is greatly influenced by the content of silicon dioxide. Water leaching process after ammoniumIncreasing sulphate the roasting roasting temperature in these literatures has little [26,28,35] effect on further is an important increasing factor the extraction resulting efficiencylow iron recovery.of iron. Table The S1results shows demonstrate the iron extractionthat it is fromnecessary various to adopt minerals, acid suchleaching as mine after tailingsammonium [28], sulphatenickel laterite roasting [26 ,in35 ]order and ilmeniteto improve [30 the], using iron ammoniumrecovery efficiency. sulfate as a roasting agent. These results implicateIt is thatindicated the iron from extraction Figure efficiency 3b that isthe either extr loweraction orof higher. manganese This situation increases may with be relatedroasting to temperature.the content of The silica leaching in the ore, efficiency which may of mangan retard theese diffusionrises from of ammonium56.4% to 99.3% sulphate as the through roasting the temperatureash layer from increases the surface from to 300 the °C center to 400 of the°C PAR.at a ro Whenasting the time silica of 240 is high, min. the The recovery leaching rate behavior of iron of is manganeselow [26,28,35 differs], and vicegreatly versa from the recoverythat of iron rate ofduri ironng isthe high roasting when theprocess, content which of silicon seems is low not [ 30to, 31be]. Aboutaffected 95.6% by the Fe content can be extractedof SiO2 infrom the residue. the roasting The insensitivity product of pure of manganese FeOOH under roasting the same process conditions, to SiO2 which further verify the above-mentioned mechanism that the iron roasting is greatly influenced by the content of silicon dioxide. Water leaching process after ammonium sulphate roasting in these literatures [26,28,35] is an important factor resulting low iron recovery. The results demonstrate that it is necessary to adopt acid leaching after ammonium sulphate roasting in order to improve the iron recovery efficiency. It is indicated from Figure3b that the extraction of manganese increases with roasting temperature. The leaching efficiency of manganese rises from 56.4% to 99.3% as the roasting temperature increases Metals 2018, 8, 38 7 of 12
Metals 2018, 8, 38 7 of 12 from 300 ◦C to 400 ◦C at a roasting time of 240 min. The leaching behavior of manganese differs greatly fromlayer thatcan ofbe ironascribed during to thethe roastingfact that process,the mang whichanese seems dioxide not was to be sulphated affected byinto the soluble content manganese of SiO2 in thesulphate residue. by SO The2 gas insensitivity generated of from manganese the reactions roasting (Equations process (7) to SiOand2 (11)).layer Compared can be ascribed with tothe the liquid fact thatammonium the manganese sulphate dioxide in the roasting was sulphated process, into SO soluble2 gas more manganese easily diffused sulphate through by SO2 SiOgas2 generatedlayer into fromthe unreacted the reactions residue (Equations surface. (7) and (11)). Compared with the liquid ammonium sulphate in the roastingThe process,extraction SO process2 gas more of iron easily and diffused manganese through from SiO pyrolusite2 layer into adsorbent the unreacted residue residue (PAR) surface. with ammoniumThe extraction sulphate processas a roasting of iron agent and can manganese be simulated from by pyrolusite so-called adsorbent a shrinking residue model. (PAR) The withsimulation ammonium resultssulphate of iron are as ashown roasting in agentFigure can S2, be showing simulated that by the so-called iron extraction a shrinking process model. is Thecontrolled simulation by the results chemical of ironreaction are on shown the PAR in Figure surface S2, at showingthe roasting that temperature the iron extraction of 275 °C, process and is ◦ iscontrolled controlled by bythe the diffusion chemical of reactionthe reactants on the through PAR surface the inert at or the product roasting layer temperature at 300–375 of °C. 275 TheC, ◦ andapparent is controlled activation by theenergy diffusion was estimated of the reactants as 20.56 through kJ/mol the (Figure inert or 4), product supporting layer atthe 300–375 diffusionC. Themechanism apparent for activation iron extraction. energy Figure was estimated S3 shows as th 20.56e simulation kJ/mol (Figureresults 4of), the supporting manganese the extraction diffusion mechanismprocess. From for Figure iron extraction. S3, the manganese Figure S3 showsleaching the process simulation is controlled results of by the both manganese reactant extraction diffusion process.and surface From chemical Figure S3,reaction the manganese at a roasting leaching temp processerature is of controlled 300–375 by°C. both When reactant the temperature diffusion and is ◦ surfaceincreased chemical to 400 °C, reaction the manganese at a roasting extraction temperature rate is of limited 300–375 byC. SO When2 diffusion the temperature though the isinert increased layer. ◦ toFrom 400 theC, Figure the manganese 4, the apparent extraction activation rate is limitedenergy byof SOmanganese2 diffusion recovery though was the inertdetermined layer. From as 29.52 the FigurekJ/mol.4 , the apparent activation energy of manganese recovery was determined as 29.52 kJ/mol.
(a) (b)
Figure 4. The determination of apparent activation energy of (a) iron and (b) manganese. Figure 4. The determination of apparent activation energy of (a) iron and (b) manganese.
3.3. Effect of Conditions Applied for Roasting and Acid Leaching 3.3. Effect of Conditions Applied for Roasting and Acid Leaching
3.3.1. Effect of Ammonium Sulphate: PAR Mass Ratio The dosage of ammonium sulphate is the essentialessential factor for the roasting process to obtain higher manganese and iron recovery efficiency. The effect of NH ) SO : PAR mass ratio on the higher manganese and iron recovery efficiency. The effect of (NH4)2SO4: PAR mass ratio on the manganese and iron extraction rate is shown in Figure5 5.. OtherOther conditionsconditions werewere as as follows: follows: 450450 ◦°CC of roasting temperature,temperature, 3030 min min of of roasting roasting time, time, 90 90◦C °C of leachingof leaching temperature, temperature, 60 min 60 ofmin leaching of leaching time, andtime, sulphuric and sulphuric acid concentration acid concentration of 0.5 of M. 0.5 M. It cancan bebe seen seen from from Figure Figure5, the 5, ironthe extractioniron extraction increased increased with increasing with increasing the ammonium the ammonium sulphate dosage.sulphate This dosage. is because This is increasing because increasing the amount the of amount ammonium of ammonium sulphate enhanced sulphate the enhanced drive force the ofdrive the force of the diffusion of NH ) SO through the inert layer. As the ratio of ammonium sulphate to diffusion of (NH4)2SO4 through the inert layer. As the ratio of ammonium sulphate to PAR is over 6:1,PAR the is extractedover 6:1, iron the increaseextracted slowly, iron andincrease about slowly, 97.6% Fe and has about beenextracted. 97.6% Fe Manganese has been extractionextracted. seemsManganese to be extraction greatly influenced seems to be by greatly the ammonium influenced sulphate-to-PAR by the ammonium ratio. sulphate-to-PAR The leaching ratio. efficiency The increasedleaching efficiency from 51.5% increased to about from 97.0%, 51.5% when to theabout ratio 97.0%, is increased when the from ratio 2:1 is to increased 12:1. Continuing from 2:1 increase to 12:1. inContinuing ammonium increase sulphate: in PARammonium ratio over sulphate: 12:1 does notPAR result ratio in over obvious 12:1 improvement does not result upon in manganese obvious leaching.improvement The strongupon manganese dependence leaching. of manganese The strong extraction dependence upon the of manganese dosage of ammonium extraction upon sulphate the dosage of ammonium sulphate can be attributed to more SO2 gas generated by decomposition of