PURIFICATION OF MnSO ₄ SOLUTIONS THIS INVENTION relates to purification of MnSO ₄ solutions. In particular, the invention relates to a process for purifying a MnSO ₄ solution. MnSO ₄ solutions of a high purity, i.e. with specified low levels of contaminants such as Ca, Co, Fe, Mg, Ni and Zn, and a minimum Mn concentration, are commercially important, e.g. for use in electrochemical cells and batteries. Various methods exist to purify MnSO ₄ solutions, but they tend to be cumbersome and expensive. A process for purifying a MnSO ₄ solution which is less cumbersome and more economical than conventional MnSO ₄ solution purification processes would be desirable. According to the invention, there is provided a process for purifying a MnSO4 solution, the process including precipitating impurities from the MnSO ₄ solution (i) in the presence of a stochiometric excess of fluoride anions, where said stochiometric excess of fluoride anions is calculated on the basis of the fluoride anions required to react with all Mg ²⁺ and Ca ²⁺ cations present in the MnSO4 solution as impurities to form CaF2 and MgF2, and (ii) in the presence of sulphide anions, at a pH higher than 4, producing a slurry or suspension comprising a purified MnSO4 solution as a carrier medium and a suspended precipitate which includes MnS, MnF2, CaF2 and MgF2; separating the slurry or suspension into said purified MnSO4 solution and said precipitate; reacting the precipitate with a SO4 salt (sulfate salt) other than MnSO4 in a solid-state reaction to produce recovered MnSO4 from the MnS and MnF2; and recycling the recovered MnSO4 to the MnSO4 solution which is being purified, thereby to reduce Mn losses and improve MnSO4 yield. The MnSO ₄ solution may be a pregnant leach solution. The MnSO ₄ solution may be contaminated with Ca, Co, Fe, Mg, Ni and Zn as impurities. Other contaminants may include Cu, K, Na, Si, Al, Sr and Pb. In one embodiment of the invention, the MnSO ₄ solution is a leachate obtained by a roasting and leaching process, e.g. a roasting and leaching process for extracting manganese from manganese-bearing ore as disclosed in South African Provisional Patent Application No 2022/05305. Typically, the process includes adding a base to the MnSO ₄ solution to ensure that the pH is higher than 4. The base may be NH ₄ OH, e.g. a 25% NH ₄ OH solution. Advantageously, in the process of the invention, an ammonium salt formed as a result of the addition of NH ₄ OH is decomposed downstream to form a treatable gas. Preferably, during the precipitation of the impurities from the MnSO ₄ solution, the pH is controlled at between about 5 and about 8, more preferably between about 5 and about 7. The stochiometric excess of fluoride anions may be generated in the MnSO4 solution by the addition of a stochiometric excess of a source of fluoride anions, such as a water-soluble fluoride salt or hydrofluoric acid. Preferably, the stochiometric excess of fluoride anions is generated by the addition of a stochiometric excess of a water-soluble fluoride salt, e.g. NH4F·HF, as it is typically less hazardous than hydrofluoric acid. Typically, the process includes agitating the MnSO4 solution during the precipitation of impurities from the MnSO4 solution. Precipitating impurities from the MnSO ₄ solution may include first adding a source of fluoride anions, and thereafter adding a base to the MnSO ₄ solution to ensure that the pH is higher than 4. Typically, predominantly Ca and Mg cations are precipitated from the MnSO ₄ solution after the addition of the source of fluoride anions (i.e. as CaF ₂ and MgF ₂ ) _, in addition to some MnF ₂ , with the MnF ₂ forming the major component (i.e. the component in the highest concentration) of the precipitate. However, other cations present in the MnSO ₄ solution as impurities and that form insoluble fluorides, such as Na which forms insoluble Na ₂ SiF ₆ , may also precipitate. The sulphide anions may be generated in the MnSO ₄ solution by the addition of a source of sulphide anions. The source of sulphide anions may be selected from the group consisting of MnS, (NH ₄ ) ₂ S, H ₂ S(g) and mixtures of two or three thereof. In a preferred embodiment of the invention, the source of sulphide anions is MnS. Typically, the source of sulphide anions is added to the MnSO4 solution after the addition of a base to the MnSO4 solution. Thus, typically, in at least one embodiment of the invention, precipitating impurities from the MnSO4 solution includes first adding a source of fluoride anions to the MnSO4 solution, thereafter adding a base to the MnSO4 solution to ensure that the pH is higher than 4, and thereafter adding a source of sulphide anions to the MnSO4 solution. The MnS may be added to the MnSO4 solution in a concentration of between about 2 and about 0.0001 mol MnS/litre MnSO4 solution, preferably in a concentration of between about 1 and about 0.0005 mol MnS/litre MnSO4 solution, more preferably in a concentration of between about 0.1 and about 0.001 mol MnS/litre MnSO4 solution, e.g about 0.06 mol MnS/litre MnSO4 solution. Separating the slurry or suspension into said purified MnSO ₄ solution and said precipitate may be effected using any conventional or suitable solids-liquid separation technology, e.g. filtration, gravity separation, cyclonic separation or the like. In a preferred embodiment of the invention, the slurry or suspension is separated into said purified MnSO ₄ solution and said precipitate by means of filtration. Advantageously, MnS acts as a filter aid to filter small CaF ₂ and MgF ₂ particles from the MnSO ₄ solution, and as a precipitation agent to precipitate transition elements such as Co, Fe, Ni, Cu and Zn from the MnSO ₄ solution. Typically, the precipitation of impurities from the MnSO ₄ solution in the presence of fluoride anions is effected at ambient temperature and pressure. The precipitation of impurities from the MnSO ₄ solution in the presence of sulphide anions may be effected at a temperature in the range of about 5°C to about 100°C, preferably in the range of about 30°C to about 80°C, more preferably in the range of about 50°C to about 70°C, e.g. about 60°C. The process may thus include heating the MnSO4 solution, subsequent to the addition of a base to the MnSO4 solution, and adding the source of sulphide anions, e.g. MnS, to the heated MnSO4 solution. The fluoride anions may be present in a stochiometric excess of 6 times the stochiometric amount, preferably at least 7 times the stochiometric amount, calculated on the basis of the fluoride anions required to react with all Mg ²⁺ and Ca ²⁺ cations present in the MnSO4 solution to form CaF2 and MgF2. The fluoride anions will typically be present in a stochiometric excess of no more than 9 times the stochiometric amount calculated on the basis of the fluoride anions required to react with all Mg ²⁺ and Ca ²⁺ cations present in the MnSO4 solution to form CaF2 and MgF2. Reacting the precipitate with a SO ₄ salt other than MnSO ₄ in a solid-state reaction may include drying the precipitate. Reacting the precipitate with a SO ₄ salt other than MnSO ₄ in a solid-state reaction may include comminuting the precipitate to reduce particle size. The precipitate may be comminuted to achieve a particle size distribution with a D90 of less than about 1000 µm, preferably less than about 500 µm, more preferably less than about 250 µm, e,g. less than 106 µm. Typically, the precipitate is comminuted to achieve a particle size distribution with a D10 of at least 10 µm. Reacting the precipitate with a SO ₄ salt other than MnSO ₄ in a solid-state reaction may include reacting the precipitate with (NH ₄ ) ₂ SO ₄ or NH ₄ HSO ₄ . The SO4 salt may have a particle size distribution with a D90 of less than about 1000 µm, preferably less than about 500 µm, more preferably less than about 250 µm, e,g. less than 106 µm. Typically, the SO4 salt has a particle size distribution with a D10 of at least 10 µm. The solid-state reaction between the precipitate and the SO4 salt may take place at a temperature in the range of about 375°C and about 525°C, preferably about 400°C and about 500°C, more preferably between about 425°C and about 475°C, e.g. about 450°C. When the SO4 salt is, or includes, (NH4)2SO4, MnF2 present in the precipitate may react with the (NH4)2SO4 in accordance with Reaction 1 as follows: MnF2(s) + (NH4)2SO4(s) → MnSO4(s) + NH4F·HF(g) + NH3(g) … (1) When the SO ₄ salt is, or includes, (NH ₄ ) ₂ SO ₄ , MnS present in the precipitate may react with the (NH ₄ ) ₂ SO ₄ in accordance with Reaction 2 as follows: MnS(s) + 4(NH ₄ ) ₂ SO ₄ (s) → MnSO ₄ (s) + 4SO ₂ (g) + 4H ₂ O(g) + 8NH ₃ (g) … (2) The process may include partially condensing off-gas generated by the solid-state reaction of the precipitate with the SO ₄ salt to condense and recover NH ₄ F·HF from the off-gas, and to produce cooled off-gas. The off-gas may be partially condensed at a temperature of less than about 240°C, preferably less than about 200°C, more preferably less than about 150°C, e.g. about 100°C. Typically, the off-gas is partially condensed at a temperature of at least about 25°C. The process may include recycling the NH4F·HF recovered from the off-gas to act as a source of fluoride anions thereby to provide the stochiometric excess of fluoride anions for precipitating Ca and Mg impurities from the MnSO4 solution. The process may include scrubbing the cooled off-gas with an absorbent, e.g. water, to remove NH3(g) from the cooled off-gas. The process may include scrubbing the cooled off-gas in a SO2 scrubber to desulfurize the cooled off-gas. Instead, an NH3 scrubber employed to remove NH3(g) from the cooled off-gas may also act as a SO2 scrubber. The recovered MnSO4 may be recycled to the MnSO4 solution as a recycle MnSO4 solution. The process may thus include dissolving the recovered MnSO4 in water to form the recycle MnSO4 solution. An insoluble waste stream may be produced, which may be withdrawn from the process and dumped. This waste stream may act as a bleed stream to prevent or control build-up of concentrations of Al, Ca, Co, Fe, K, Mg, Na, Ni and Zn in the process. Dissolving the recovered MnSO ₄ in water to form the recycle MnSO ₄ solution may be effected using water at ambient temperature. Dissolving the recovered MnSO ₄ in water to form the recycle MnSO ₄ solution may be effected under agitation. The invention will now be described, by way of example, with reference to the following laboratory experiments and the single drawing which shows one embodiment of a process in accordance with the invention for purifying a MnSO ₄ solution. Laboratory Experiments Several laboratory experiments were conducted to investigate various aspects of the process of the invention for purifying a MnSO4 solution. Material A 4-litre volume of a pregnant leach solution of MnSO4 with the following analysis as set out in Table 1 was used in the experiments. Table 1: MnSO4 pregnant leach solution composition (mg/l) Fluoride precipitation Fluoride precipitation was used to precipitate mainly the Ca and Mg cations from the pregnant leach solution. Other cations also precipitate as insoluble fluoride precipitates, such as Na ₂ SiF ₆ . Unfortunately, MnF ₂ also precipitates. Although MnF ₂ is about 100 times more soluble than CaF ₂ and MgF ₂ , stoichiometric addition of the fluoride anion from a source of fluoride anions, such as HF or NH ₄ F·HF, surprisingly does not provide a MnSO ₄ solution complying with battery grade specifications. There is an equilibrium and it was established that at least six, preferably seven times the stoichiometric amount of fluoride anions, calculated on the basis of the fluoride anions required to react with all Mg ²⁺ and Ca ²⁺ cations present in the MnSO ₄ solution to form CaF ₂ and MgF ₂ , is required comfortably to achieve an ultra-high purity MnSO ₄ solution. Ammonium bifluoride (NH ₄ F·HF) was chosen as the source of fluoride anions because it is less hazardous than HF solutions. However, just like HF, NH ₄ F·HF comes at a price and NH ₄ F·HF consumption and losses should thus be minimised. Furthermore, because of equilibrium, a portion of MnF ₂ also precipitates as mentioned hereinbefore, which leads to Mn losses and lower yields of MnSO ₄ . The use of expensive reagents, the formation of hazardous fluoride waste and the yield loss of Mn values can all be mitigated by implementation of at least some form of recycle. Calculations for fluoride addition The first step was to calculate the mol amount of Mg and Ca in the 4 litre MnSO4 solution, as follows: Ca = 0.593g = 0.014825 mol Mg = 1.755g = 0.072 mol Total mol (Ca + Mg) = 0.08705 mol/litre PLS. The amount of NH4F·HF required, based on a stoichiometric excess of 7 times, was then calculated as follows: NH4F·HF addition required = 7 x 0.08705 mol/litre x 57g/mol NH4F·HF x 4 litres = 138.93 g Experimental The 4 litres of the pregnant leach solution was first transferred into a 5-litre plastic polypropene beaker. To this 138.93g NH4F·HF was added while stirring. The pH dropped from about 6 or 7 to about 3. At this pH, no precipitation occurred. To this solution, suspension forming. After 2 hours of stirring, the suspension was filtered. A resulting precipitate or filter cake was washed to recycle MnSO ₄ trapped in the moist filter cake. The washed filter cake was then dried at 150°C and yielded 78.5g fluoride residue. The analysis of the washed fluoride precipitate or filter cake, i.e. residue, is provided in Table 2. Table 2: Fluoride precipitate composition (wt%) Although the fluoride precipitation removed a significant portion of the Ca and Mg from the pregnant leach solution of MnSO4, it was found that, after filtration, the remaining pregnant leach solution (i.e. filtrate) still contains Ca and Mg levels at more than 50 ppm so that the filtrate does not comply with battery grade specifications, which require Ca and Mg at less than 50 ppm, with a minimum Mn concentration of 32%. The reason for this is that some of the MgF2 and CaF2 precipitated particles are too small to filter under normal laboratory conditions. The solution to this problem proposed as part of the present invention is the addition of MnS which acts as a filter aid to filter the small CaF ₂ and MgF ₂ particles, and also acts as a precipitation agent for the precipitation of transition elements such as Co, Fe, Ni, Cu, and Zn. Sulphide precipitation Just like the fluoride precipitate forms an equilibrium, the sulphide precipitate also forms an equilibrium. Experimentally, it was found that about 0.06 mol of MnS/litre of pregnant leach solution of MnSO ₄ is enough to act as a filter aid to assist with the removal of the remaining Ca and Mg. It is also enough to precipitate all the transition elements as can be seen in the calculations below. Calculations of transition elements: The mols transition elements in the 4 litre pregnant leach solution: Co = 0.0983g = 0.0017 mol / litre Fe = 0.0139g = 0.00025 mol / litre Ni = 0.0554g = 0.00095 mol / litre Zn = 0.0023g = 0.000034 mol / litre Total mols of transition elements per 4 litres of pregnant leach solution = 0.011736 mols Freshly precipitated MnS was prepared via the reaction of Na ₂ S (60%) and battery grade MnSO ₄ to produce a suspension of MnS precipitate and Na ₂ SO ₄ (aq). The MnS precipitate was filtered from the suspension and washed from any Na ₂ SO ₄ contamination. A total of 0.24 mol of the moist freshly precipitated MnS was added to the remainder of the 4 litres of the pregnant leach solution and heated to 60°C. After 2 hours of stirring at this temperature, a black precipitate was filtered to form a filter cake. The filter cake was washed to remove and recycle trapped MnSO ₄ , and then dried at 150°C, yielding 54g sulphide residue. Table 3 provides the analysis of the sulphide precipitate. It is believed that the amount of MnS per litre pregnant leach solution can be further optimised to reduce the amount. Table 3: Sulphide Precipitate composition (wt%) The final, purified MnSO ₄ solution had the analysis as set out in Table 4. Table 4: Final MnSO ₄ solution after fluoride and sulphide precipitation (mg/l) The last row in Table 4 is the maximum allowable impurities levels for battery grade MnSO4.H2O, for Ca, Co, Fe, Mg, Ni and Zn. The third row in Table 4 is the level of Ca, Co, Fe, Mg, Ni and Zn impurities after fluoride and sulphide precipitation. Recycling of reagents From Table 1 the total Mn amount in the pregnant leach solution can be calculated as follows: 4 litres x 127.6 g/l = 510.4 g Mn. The Mn units lost to the fluoride and sulphide precipitates can also be calculated as follows: Fluoride precipitate: 78.5g x 37.7% = 29.6g = 5.8% of the starting MnSO ₄ solution. Sulphide precipitate: 54g x 49.5% =27g = 5.3% of the starting MnSO ₄ solution. The fluoride precipitate and the sulphide precipitate were separately dry milled to -106 um. To 67.2g of the fluoride precipitate, 110g (NH ₄ ) ₂ SO ₄ -106µm was added, blended, and fired in a 3Cr12 stainless steel tube at 450°C. Calcined product from the tube was soaked for 3 hours at temperature, and after cooling to room temperature yielded 101.6 g white cake. It was found that almost all of this product is water soluble. The MnF ₂ and the (NH ₄ ) ₂ SO ₄ reacted in the fired tube according to the following solid-state reaction: MnF2(s) + (NH4)2SO4(s) = MnSO4(s) + NH4F.HF(g) + NH3(g) The NH4F·HF sublimes and can be condensed below about 240°C, e.g. below 100°C to collect approximately 90 - 99% of the available fluorides. The NH3(g) can be scrubbed and almost all the MnSO4(s) can be recycled back to the pregnant leach solution of MnSO4. To 20g of the sulphide precipitate, 130g (NH4)2SO4 -106µm was added, blended, and fired in a 3Cr12 stainless steel tube at 450°C. Calcined product from the tube was soaked for 3 hours at temperature, and after cooling to room temperature yielded 29.6 g white cake. It was found that almost all of this product is water soluble. The MnS and the (NH ₄ ) ₂ SO ₄ reacted in the fired tube according to the following solid-state reaction: MnS(s) + 4(NH ₄ ) ₂ SO ₄ (s) = MnSO ₄ (s) + 4SO ₂ (g) + 4H ₂ O(g) + 8NH ₃ (g) 10g samples of the white cakes from both calcination products were dissolved in 50 ml water, filtered, and analysed. The analysis is provided in Table 5. Table 5: MnSO ₄ solutions obtained after dissolution of calcination products (mg/l) As will be noted, based on the analysis set out in Table 5, the MnSO4 solutions obtained from the solid-state reaction of the fluoride precipitate and the sulphide precipitate with (NH4)2SO4 are suitable for recycling to the pregnant leach solution of MnSO4 used at the start of the experiment, to recover Mn values. Referring to the single drawing, reference numeral 10 generally indicates a process in accordance with the invention for purifying a MnSO4 solution. The process 10 is a continuous process and includes a precipitation stage 12 comprising a fluoride precipitation vessel 14, a pH adjustment vessel 16 and a sulphide precipitation vessel 18. The process 10 further includes a first filter 20, a drying and comminuting stage 22, a rotary kiln 24, a dissolution vessel 26, a second filter 28, a cooler condenser 30 and an off-gas scrubber 32. A MnSO ₄ solution feed line 34 leads to the fluoride precipitation vessel 14, which is also joined by an NH ₄ F·HF feed line 36. The fluoride precipitation vessel 14 is provided with a stirrer 38. A solution transfer line 40 leads from the fluoride precipitation vessel 14 to the pH adjustment vessel 16, which is also provided with a stirrer 42. An NH ₄ OH solution feed line 44 leads into the pH adjustment vessel 16, whereas a suspension transfer line 46 leads from the pH adjustment vessel 16 to the sulphide precipitation vessel 18. The sulphide precipitation vessel 18 is provided with a stirrer 48, a steam heating coil 50 and a MnS feed line 52. A suspension transfer line 54 leads from the sulphide precipitation vessel 18 to the first filter 20, which is provided with a purified MnSO ₄ solution withdrawal line 56 and a filter cake transfer line 58. The filter cake transfer line 58 leads to the drying and comminuting stage 22, which is provided with a comminuted precipitate withdrawal line 60 which leads to the rotary kiln 24. The comminuted precipitate withdrawal line 60 is joined by a (NH4)2SO4 feed line 62. The rotary kiln 24 is a fired kiln which is provided with an off-gas withdrawal line 64 and a calcined precipitate withdrawal line 66, which leads to the dissolution vessel 26. The dissolution vessel 26 is provided with a stirrer 68 and a water feed line 70. A suspension withdrawal line 72 leads from the dissolution vessel 26 to the second filter 28, which is provided with a solids waste stream withdrawal line 74 and a MnSO4 solution recycle line 76 which joins the MnSO4 solution feed line 34. The process 10 is used to purify a pregnant MnSO4 leach solution or other MnSO4 solution contaminated inter alia with Ca, Co, Fe, Mg, Ni and Zn as impurities. The pregnant MnSO ₄ leach solution is fed by means of the MnSO ₄ solution feed line 34 into the fluoride precipitation vessel 14. A source of fluoride anions, namely NH ₄ F·HF is fed by means of the NH ₄ F·HF feed line 36 into the fluoride precipitation vessel 14 and the stirrer 38 is used to mix the two feed streams thoroughly, producing a well-mixed solution. Sufficient NH ₄ F·HF is fed by means of the NH ₄ F·HF feed line 36 to ensure a stochiometric excess of fluoride anions present in the fluoride precipitation vessel 14, equivalent to seven times the fluoride anions required to react with all Mg ²⁺ and Ca ²⁺ cations present as impurities in the pregnant MnSO ₄ leach solution. Although no visible fluoride precipitation takes place in the fluoride precipitation vessel 14, the pH of the well-mixed solution drops from about 6 or 7 to about 3. This well- mixed solution at a pH of about 3 is then transferred by means of the solution transfer line 40 to the pH adjustment vessel 16, where a base, namely sufficient NH ₄ OH in the form of a 25% NH ₄ OH aqueous solution, is fed into the pH adjustment vessel 16 by means of the NH ₄ OH solution feed line 44 to raise the pH of the solution in the pH adjustment vessel 16 to about 5. At the elevated pH in the pH adjustment vessel 16, precipitation of fluorides such as CaF2, MgF2 and, undesirably, MnF2, commences. The stirrer 42 is used to ensure that a suspension is formed and maintained in the pH adjustment vessel 16. The pH adjustment vessel is sized to provide an average residence time of about 2 hours, whereafter the agitated suspension is transferred from the pH adjustment vessel 16 to the sulphide precipitation vessel 18 by means of the suspension transfer line 46. Particulate MnS is fed into the sulphide precipitation vessel 18 by means of the MnS feed line 52 and the suspension inside the sulphide precipitation vessel 18 is agitated by means of the stirrer 48, and heated to about 60°C by means of the steam heating coil 50. In the sulphide precipitation vessel 18 sulphides precipitate, including sulphides of Ca, Mg, Co, Fe, Ni and Zn. The CaS and MgS precipitates are thus in addition to the CaF2 and MgF2 precipitates that formed in the pH adjustment vessel 16. The particulate MnS is fed into the sulphide precipitation vessel 18 at a ratio of about 0.06 mol of MnS per litre of suspension fed into the sulphide precipitation vessel 18 by means of the suspension transfer line 46. The sulphide precipitation vessel 18 is sized to provide an average residence time of about 2 hours, whereafter the agitated suspension, comprising a suspended black precipitate, is transferred by means of the suspension transfer line 54 to the first filter 20, where the suspension is separated into a purified MnSO ₄ solution or filtrate which is withdrawn by means of the purified MnSO ₄ withdrawal line 56 and a precipitate or filter cake, which includes MnF ₂ , CaF ₂ and MgF ₂ as well as MnS, CaS and MgS and transition metal sulphides and/or fluorides, which is removed by means of the filter cake transfer line 58. Advantageously, the MnS acts as a filter aid to filter small precipitated CaF ₂ and MgF ₂ from the MnSO ₄ solution, whilst also acting as a precipitation agent for transition elements such as Co, Fe, Ni, Cu and Zn. If desired or necessary, the filter cake may be washed (not shown) with water in conventional fashion, e.g. to remove trapped MnSO ₄ , with filter cake wash water being recycled to the fluoride precipitation vessel 14 or to the filter 20 or to the dissolution vessel 26. In the drying and comminuting stage 22, the filter cake or precipitate is dried in conventional fashion, e.g. at about 150°C and then comminuted, typically by means of dry milling, to have a D90 particle size distribution of less than about 106μm. The dry, comminuted precipitate is withdrawn by means of the comminuted precipitate withdrawal line 60 and fed to the fired rotary kiln 24. Particulate (NH4)2SO4, also with a particle size distribution with a D90 of less than about 106μm, is also fed to the rotary kiln 24 by means of the (NH4)2SO4 feed line 62. In the rotary kiln 24, the dried, comminuted precipitate and the particulate (NH4)2SO4 are thoroughly admixed and heated to an elevated temperature of about 450°C, leading to solid-state reactions between the MnF2 and the MnS present in the dried, comminuted precipitate on the one hand, and the (NH4)2SO4 on the other hand, according to Reactions (1) and (2) as hereinbefore described, to produce MnSO4(s). After a suitably long time at the elevated temperature, e.g. about 3 hours, a solids material, i.e. calcined precipitate comprising MnSO4(s), is withdrawn from the rotary kiln 24 by means of the calcined precipitate withdrawal line 66 and fed to the dissolution vessel 26. Water is also fed into the dissolution vessel 26 by means of the water feed line 70 with a resultant suspension formed in the dissolution vessel 26 being agitated by means of the stirrer 68. A recycle MnSO ₄ solution is formed inside the dissolution vessel 26 as a result of the dissolving of the MnSO ₄ (s) in the water. A suspension comprising the recycle MnSO ₄ solution is withdrawn from the dissolution vessel 26 by means of the suspension withdrawal line 72 and fed to the second filter 28, where insoluble impurities are separated from the recycle MnSO ₄ solution and withdrawn by means of the solids waste stream withdrawal line 74. The recycle MnSO ₄ solution is transferred from the second filter 28 to the MnSO ₄ solution feed line 34, by means of the MnSO ₄ solution recycle line 76. Off-gas from the rotary kiln 24 is withdrawn by means of the off-gas withdrawal line 64, and cooled and partially condensed in the cooler condenser 30. Plant cooling water is used in the cooler condenser 30 partially to condense the off-gas at a temperature of about 90°C. Condensed NH4F·HF from the cooler condenser 30 is transferred by means of the NH4F·HF recycle line 78 to join the NH4F·HF feed line 36. In this way, about 90% of the fluoride anions added to the process 10 is recovered and recycled to the fluoride precipitation vessel 14. Cooled off-gas from the cooler condenser 30 is transferred by means of the cooled off-gas line 80 to the off-gas scrubber 32, which employs water fed by means of the water feed line 82 to scrub NH3(g) and SO2(g) from the cooled off-gas. Scrubbed off-gas is vented from the off-gas scrubber 32 to the atmosphere by means of the vent line 84, whereas excess ammoniacal scrubbing solution is withdrawn by means of the scrubber solution withdrawal line 86. Although described as a continuous process, as will be appreciated, the process 10 can be operated on a batch basis or on a semi-batch basis. For example, the fluoride precipitation vessel 14, the pH adjustment vessel 16 and the sulphide precipitation vessel 18 can be combined into a single vessel operated on a batch basis. In the process 10, as illustrated, a very large proportion of the fluoride anions is advantageously recycled. By including process steps to inhibit Mn losses and to recycle Mn (e.g. by means of the rotary kiln 24, the dissolution vessel 26 and the second filter 28), the process 10, as illustrated, increases MnSO ₄ yield. Advantageously, the process of the invention can produce a battery grade MnSO ₄ solution with less than 1 ppm Co, Fe, Ni and Zn, and less than 15 ppm Ca and Mg, from a pregnant MnSO ₄ leach solution.