Journal of Chemical Technology Metallurgy, 1, 2015 Journal of Chemical Technology andand Metallurgy, 50,50, 1, 2015, 26-34 INVESTIGATION OF NITRIC ACID BENEFICIATION OF LOW GRADE PHOSPHORITES FROM CENTRAL KYZYLKUM Bokhodir E. Sultonov, Shafoat S. Namazov, Bakhtiyar S. Zakirov Institute of General and Inorganic Chemistry , Academy of Sciences of Uzbekistan 77a, st. Mirzo-Ulugbek, 100170, Tashkent, Uzbekistan E -mail: [email protected] Received 03 September 2014 Accepted 05 December 2014 ABSTRACT With the purpose of obtaining chemical concentrated phosphates, suitable for quality fertilizers manufacture, a process of chemical beneficiation of poor phosphorites from Central Kyzylkum was investigated. The influence of norm of nitric acid on dressability phosphorites is studied and рН media are defined in which a passage of Р2О5 was excluded in liquid phase. Optimum concentrations for the repulping solution of Ca(NO3)2 at which the concentration of the received solution will be over, were defined. Influence of the quantity and temperature of washing water on the extent of removal of Ca(NO3)2 from the phosphorus concentrates were investigated and the optimum quantity and temperature of washing water where content of Ca(NO3)2 in phosphorus concentrates will be minimum was defined. The possibility for obtaining of chemical beneficiation of phosphorus concentrates by interaction of Central Kyzylkum phosphorites with aquafortis was shown. The chemical beneficiation phosphorus concentrates meets the requirements for sulfuric acid extraction with obtaining of extraction phosphoric acid and phosphorous containing fertilizers on its base. Keywords: poor phosphorites, nitric acid, phosphorus concentrate, calcium module, degree of calcinations, extent of removal. INTRODUCTION In Uzbekistan the phosphorites of Central Kyzylkum became the basic raw materials for production of phosphorus containing fertilizers. These phosphorites are with poorest content of the basic component - phosphorus (16.2 % Р2О5). In the world practice is known, that the phosphate raw materials, applicable for sulfur acid extraction should be with content of P2O5 not less than 24.5 %, CO2 should be not more than 8 %, (R2O3 : P2O5).100 can not be more than 12 %, (MgO : P2O5).100 can not be more than 7 - 8 %. The recommended value of the calcium module (СаО : P2O5) is 1.6 and chlorine is not more than 0.04 % in the raw materials. Therefore the poor raw material has to be enriched. The most accepted method for enrichment is flotation. However, the Kyzylkum phosphate rock, due 26 to along the close mutual germination of phosphate minerals and calcite, the attempt to enrich them through flotation did not lead to positive results. The value of the calcium module (СаО:P2O5) is 2.85. The content of chlorine reaches 0.10 - 0.25 %, that leads to intensive corrosion of the equipment [1]. So, the Kyzylkum phosphorite plant developed the manufacture of enriched phosphorites by their washing out of chlorine and burning in fluidized process [2, 3]. During the proximate years an expanding production of washed and burned concentrate to 716 thousand tons per year with the content of P2O5 not less than 26 % is provided. The main drawbacks of the existing technology of enrichment are the following: The high value of the calcium module (2.0 - 2.1) in the washed and burned concentrate, as removal of the Bokhodir E. Sultonov, Shafoat S. Namazov, Bakhtiyar S. Zakirov free CaO formed at decomposing of lime carbonate, is not provided. A considerable amount of out of balance ores the so-called “mineral masses” is dropped out in the ore’s sorting and screening operations, having phosphate with initial content of Р2О5 less than 16 % and fraction of +5 mm. Annually more than 300 thousand tons mineral masses is piled up. Currently we have more than 6 million tons mineral mass, which is not used in production of mineral fertilizers. Losses of phosphate anhydride reach 15-25 % in the tails of the flush of ore out of chlorine from the initial mass of the concentrate [4]. These slime phosphorites also are not used in any way. The process of enrichment is highly energy intensitive. In [5 - 7] processes of chemical enrichment of phosphorites from Central Kyzylkum with dilute solutions of nitric, sulfuric and hydrochloric acids, and as well as with nitric acid solutions of calcium and magnesium nitrates, were considered. The main drawbacks of the developed technologies are the following: plentiful foaming, process duration, low filtration rate of the nitric acid phosphate suspension, formation of an enormous amount of acid solutions, which create some technological difficulties at processing. In [8] the chemical beneficiation of Kyzylkum’s phosphorites with organic acids was investigated. Under the optimum conditions of beneficiation of phosphorites, containing 16.33 % Р2О5, 17.23 % СО2 and 47.13 % СаО, phosphorus concentrate with content 24.52 - 25.78 % Р2О5, which is suitable for sulfuric acid extraction was obtained. The main drawbacks of the developed technology were plentiful foaming, using huge equipment for embodiment of the beneficiation process and requirement of expensive sulfuric acid for the regeneration of organic acids. In [9] a technology for chemical beneficiation of high calcareous contents of Kyzylkum’s phosphorites, which included processing of phosphate raw material (PRM), containing 17-18 % Р2О5, with nitric acid of concentration 45-60 % taken in amount of 90-110 % from stoichiometry to СаСО3, with following repulpation of the recycled solution, containing 5-25 % Са(NO3)2, at mass ratio of phosphate raw material to Са(NO3)2 solution equal to 1:(2.0 -3.5), sedimentation of the formed nitrophosphate suspension for 5 - 10 min, as well as wet cake washing with water and product drying, was developed. The weaknesses of this method are the low yield of Р2О5 (56 -60 %), greater passage of Р2О5 into the liquid phase, heavy filtration of the nitrophosphate suspension and the formation of a huge volume of diluted solution, which demands an enormous heating for its processing into nitrogen phosphate calcium fertilizers. The above presented investigation of the more acceptable methods for beneficiation of high calcareous Kyzylkum’s phosphorites is quite actual problem at present. Previously we studied the chemical enrichment of the mineral mass, which is the waste of thermal beneficiation of phosphorites of Kyzylkum [10] with nitric acid and obtained data concerning the possible producion of phosphorus concentrate for acid processing. Subsequent systematic research we conducted also on nitric acid beneficiation of low grade phosphorites and obtaining chemical phosphorus concentrate fully suitable for wet-processing of phosphoric acid and new types of highly concentrated unary and complex fertilizers based on it [10 -13]. EXPERIMENTAL Materials For the experiments a low grade phosphorite, containing (mass %): 17.52 - Р2О5, 47.53 - СаО; 15.23 - СО2, 2.00 - SO3; 1.98 - F; 1.75 - MgO; 0.97 - Al2O3; 0.56 Fe2O3; СаО:Р2О5 = 2.71, 58.78 % of nitric acid and different concentrations of Ca(NO3)2 solutions were used. Formulas for calculations The mass of nitric acid for its various norms, based on the CaO in the initial phosphorite we determined by the formula: (1) where rite; is the mass of the initial phospho- is the mass fraction of CaO in the initial phosphorite; is the norm of HNO3 and 58.78 is the concentration of HNO3; 2.25 is the ratio of the molar mass of HNO3 and CaO in the reaction: CaO+2HNO3=Ca (NO3)2 + H2O (2) The norm of nitric acid from stoichiometry to CaO was varied in a range from 40 tо 60 %. 27 Journal of Chemical Technology and Metallurgy, 50, 1, 2015 The degree of decarbonization was calculated by the formula: (3) where is the mass of the samples of phosphorusconcentrates, is the initial mass of phosphorite, is the mass fraction of CO2 in the samples of obtained phosphorus concentrates and is the mass fraction of CO2 in the source of phosphorus. The washing degree of phosphorus-concentrates was calculated according to: where concentrate; (4) is a sample’s mass of phosphorusis the mass of the initial phosphorite; is the mass fraction of CaO in the initial phosphorite; is the mass aqua form of CaO in the of phosphorus concentrate; is the norm of HNO3; is the mass of NH3; 4.82 is the ratio of the molar masses of Са(NO3)2 and NH3 in the reaction: Ca(H2PO4)2 + Ca(NO3)2 + 2NH3 = 2CaHPO4 + 2NH4NO3 (5) 2.93 is the ratio of molar masses of Са(NO3)2 and CaO. Experimental procedure The interaction of the phosphate raw material with nitric acid was performed at 35-40°C in a glass reactor, equipped with a stirrer. The reactor was charged with nitric acid and a suitable amount (25 g) of PRM. The latter was fed in portions within 3-4 min. Partial decomposition and decarbonization of the phosphate raw materials, occurred in the reactor. After 20 minutes the resulting pulp was treated with gaseous ammonia under pH control (pH 3) to avoid P2O5 transition into a liquid phase. The differently concentrated solutions of calcium nitrate stayed at vigorous stirring in the reactor. The mass ratio of phosphorus to the calcium nitrate solution was in the range of 1:(2.0 - 3.0). The resultant slurry was separated by filtration under vacuum. The 28 wet phosphorite concentrate was washed with water in a mass ratio of PRM:H2O = 1:1.5. The wet phosphorus concentrates were dried at 100 - 105°C. However, in our investigation the influence of nitrate calcium concentration in the repulpating solution on the phosphorus concentrate quality and on the obtaining of more concentrated solution of Ca(NO3)2, the concentration repulpating solution was varied in a range from 5 tо 25 %. The influence of the water quantity on the phosphorus concentrate quality was studied by changing the mass ratio of PRM:Н2О from 1:1 tо 2:1. For investigation of the water temperature influence on phosphorus concentrate quality, the wet phosphorus concentrate was washed one-fold by water at different temperatures with mass ratio of PRM : Н2О = 1:1.5. The wet phosphorus-concentrate was dried at 100 - 1050С. Methods for analysis The dried precipitate and the filtrate were subjected to chemical analyses as follows: all forms of P2O5 [total (t), acceptable by citric acid (ac.c.a.) and acceptable by EDTA (ac. EDTA)] were determined by the calorimetric method on calorimeter CPhC-3 ((l 440 nm) in the form of an yellow phosphoro-vanadio-molybdenum complex compound [14]. The total (t) and water solubile (w.s.) forms of CaO were determined by the volume complexometric titration with 0,02 N EDTA in the presence of indicator fluorene or chrome navy-blue [14]. The form of N total (t) was determined by the Kjeldahl’s method [15]. The СО2 total (t) was determined by dissolution of carbonates with hydrochloric acid (10 % HCl). The volume of СО2t. was calculated by the difference between the total amount of CO2 and the volume of air which has remained after the absorption of the CO2 by 40 % solution of potassium hydroxide [16]. The pH of the nitrophosphate suspension was controlled with a pH-150MI (Russian Federation, 2013). RESULTS AND DISCUSSION Influence of the norm of nitric acid and pH of the medium on the phosphorus concentrate quality [10] The norm of nitric acid was taken according to CaO 45, 50 and 60 %. The acid nitric calcium phosphate solution was treated with gaseous ammonia under pH control 2.5; 3.0; 3.5; 4.0 and then it was carried out on the basis of experiments. The laboratory tests results are shown in Table 1. Bokhodir E. Sultonov, Shafoat S. Namazov, Bakhtiyar S. Zakirov СО2t СаО: Р2О5 Degree of Р2О5 passege into liquid phase The extent of removal of Са(NO3)2 from phosph.concen.,% 1.64 2.15 93.46 1:3,0 3.0 3.5 4.0 2.50 2.52 2.55 2.43 2.45 2.48 2.52 1.66 1.67 1.70 1.62 1.60 1.63 1.64 3.02 - 93.71 93.87 94.01 94.53 94.78 94.89 95.02 CaOtotal CaOw.s. 2.46 0.87 0.91 0.93 0.86 0.80 0.83 0.85 CaO ac.c.a 0.94 7.14 40.89 18.49 1.75 7.06 41.01 18.50 1.61 6.93 41.09 18.49 1.52 7.16 38.86 17.91 1.72 7.53 40.52 18.41 1.61 7.25 41.06 18.55 1.50 7.18 41.12 18.55 1.40 Norm of HNO3 for СаО = 50% P2O5ac.EDTA 7.04 10.92 10.84 10.66 10.82 11.36 11.15 11.04 P2O5ac.c.a 10.81 24.67 24.56 24.22 23.99 25.36 25.19 25.01 P2O5t. 24.03 3.0 3.5 4.0 2.5 pH 2.5 1:2.5 Ratios PRM: solution Са(NO3)2 Nt. Table 1. Influence of pH on the composition of the phosphorus concentrate obtained at various norms of HNO3 and ratios of PRM:solution of Са(NO3)2. Norm of HNO3 for СаО = 45% 2.5 39.41 3.0 3.5 4.0 2.5 25.48 26.25 26.10 26.07 25.58 11.65 11.88 11.78 11.73 11.66 7.83 7.99 7.92 7.88 7.82 0.97 0.92 0.96 1.01 0.94 2.25 2.32 2.36 2.41 2.21 1.52 1.52 1.54 1.56 1.49 3.25 4.05 94.27 94.41 94.62 94.71 94.59 1:3,0 3.0 3.5 4.0 26.50 26.41 26.36 12.06 11.99 11.94 8.07 39.62 18.56 1.71 0.85 8.00 39.88 18.64 1.62 0.91 7.95 40.33 18.81 1.50 0.90 Norm of HNO3 for СаО = 60% 2.27 2.31 2.35 1.50 1.51 1.53 - 94.97 95.05 95.21 2.5 3.0 3.5 4.0 2.5 25.50 26.70 26.61 26.52 25.41 26.96 26.87 26.74 11.66 12.18 12.10 12.03 11.64 12.32 12.25 12.15 7.84 8.18 8.12 8.06 7.84 8.29 8.23 8,16 2.15 2.18 2.21 2.24 2.09 2.11 2.14 2.17 1.47 1.48 1.49 1.50 1.44 1.45 1.46 1.47 4.35 5.07 - 93.44 93.76 93.85 94.03 94.14 94.51 94.67 94.78 1:3,0 3.0 3.5 4.0 37.48 39.56 39.65 39.78 36.59 39.22 39.26 39.31 It is seen that under pH control (pH 2.5 of pulp), Р2О5 is passed into liquid phase. In addition its value is increased with raising the norm of nitric acid and with raising the ratio of PRM: Са(NO3)2 solution. This fact shows that under pH 2.5 monocalcium phosphate has not changed into dicalcium phosphate in above mentioned reaction (2) yet. For pH of pulp 3,0 and more, there is not Р2О5 in the liquid phase, which is evidenced on finishing the interaction amongst Ca(H2PO4)2, Ca(NO3)2 and NH3. With increasing of pH from 2.5 tо 3.0 the content of Р2О5 increases from 0.64 tо 1.55 % in the phosphorus concentrate, depending on the conditions of experiments. With further increasing of pH from 3.0 tо 4.0, the content of Р2О5 decreases slightly in the phosphorus concentrate. Increasing of some contents of Р2О5 and decreasing the value of the calcium module 18.09 18.50 18.62 18.76 17.90 1.87 1:2,5 1:2,5 38.77 39.81 40.19 40.67 38.11 18.13 17.61 18.54 18.52 18.52 17.29 18.47 18.42 18.40 1.91 1.86 1.82 1.75 1.83 2.30 2.19 2.08 2.00 2.17 1.97 1.81 1.73 1.22 1.08 1.05 1.01 1.16 0.98 0.93 0.92 (СаО:Р2О5) in the phosphorus concentrate samples at the same HNO3 norm and pH of the pulp with raising the ratio of PRM:solution of Са(NO3)2 is also observed. This is explained, in all probability, with increasing of the extent of removal of Са(NO3)2 from the phosphorus concentrate. The increasing of the norm of НNO3 from 45 to 60 % contributes raising of Р2О5 content in the phosphorus concentrate from 24.67 tо 26.70 % and from 25.36 tо 26.96 %, respectively, under рН 3.0 and ratio of PRM:solution of Са(NO3)2 1:2.5 and 1:3.0. The value of the calcium module, which is important, indicates that the phosphorus concentrate quality mainly depends on the norm of НNO3. The dependence of the Р2О5 contents in the phosphorus concentrate and the value of the calcium module from the norm of НNO3 at the investigated ratios of PRM:solution of Са(NO3)2, is presented in Fig. 29 Journal of Chemical Technology and Metallurgy, 50, 1, 2015 2.71 2.71 1.66 1.66 2 Content of Р2О5,% 26.67 1.62 26.96 1.60 26.70 26.50 26.17 1.60 1.58 1 1.56 26.25 1.54 25.67 25.17 1.52 25.36 1.50 1.52 1.50 3 1.48 24.67 4 24.67 45 50 Norm of HNO3, % 1.48 1.46 1.45 17.52 0 Ratio of СаО:Р2О5 27.7 1.44 60 Fig. 1. Change of the Р2О5 content and the value of the calcium module in the phosphorus concentrate in dependence of the norm of НNO3 at рН 3; 1,3- ratio of PRM:solution of Са(NO3)2 = 1:2.5; 2,4- ratio of PRM:solution of Са(NO3)2 = 1:3.0. 1. It should be noted that the content of dissolved calcium is also a quality index of the phosphorus concentrate. The content of CaOw.s. in the phosphorus concentrate does not have to be more than 1.5 %, in recalculation of Са(NO3)2 4.4. This creats some technological difficulties in acid processing of phosphorus concentrate for fertilizers, because at Са(NO3)2 more than 4.4 % it starts to cake because of its high hygroscopicity. It can be seen from the Table 1, that at the studied conditions, the content of CaOw.s. is varied in the range 1.4 - 2.3 %. The concentration of Са(NO3)2 obtained in the solution is 13.32 - 20.41 %, which demands an enormous quantity of heat for processing of diluted nitrate calcium solution for NСа-fertilizers. In order to find the optimal conditions for separating the calcium nitrate from the calcium nitrophosphate solution and limit it in the phosphorus concentrate, where the content of CaOw.s. should be < 1.5 %, and obtain a concentrated by-product - solution of calcium nitrate, we studied the influence of the concentration of the repulped solution, as well as the amount and temperature of the washing water for obtaining high quality phosphorus concentrate. Influence of the repulped solution on the quality phosphorus concentrate [11] The laboratory tests results of this investigation are shown in Table 2. 30 It is seen that lower concentration of the calcium nitrate solution leads to higher extent of removal of the calcium nitrate from phosphorus concentrate. It is determined also that the calcium nitrate is very water-soluble. However, the problem of utilization of the diluted solution formed at leaching of the acid pulp appeared. That is why we needed an optimal concentration of the calcium nitrate for leaching of acid pulp, which as phosphorus concentrate would be the best and formed more concentrated solution of Са(NО3)2. At leaching of the acid pulp with 5 % solution of calcium nitrate with a ratio of PRM:solution of Са(NO3)2 = 1:(2.0-2.5), the extent of removal of calcium nitrate is 91.65 - 94.10 % (at norm of HNO3 - 45 %). At norm of HNO3 50 % the extent of removal of calcium nitrate from the phosphorus concentrate is 92.75 - 94.93 %. Under these conditions the best phosphorus concentrate is obtained. The content of Р2О5 is 24.55 - 26.40 % and the value of the calcium module equals 1.51 - 1.68. For leaching the acid pulp with a 10 % solution of calcium nitrate with a ratio of PRM:solution of Са(NO3)2 = 1:(2.0-2.5), the extent of removal of the calcium nitrate is 91.34 - 93.71 % (at norm of HNO3 - 45 %). At norm of HNO3 50 % the removal of calcium nitrate from the phosphorus concentrate is somewhat increased and varies in a range 92.00 - 94.41 %, the content of Р2О5 is 25.63 - 26.25 %, the value of the calcium module Bokhodir E. Sultonov, Shafoat S. Namazov, Bakhtiyar S. Zakirov equals 1.52 - 1.58. Further increase of the concentration of Са(NО3)2 (15 and 20 %) solution leads to decrease of the extent of removal of calcium nitrate from phosphorus concentrate, raising of the calcium module and for reduction of the Р2О5 content in the latter. The data in Table 2 show, that at norm of НNО3 50 %, the content of P2O5 is increased notably and the calcium module is decreased. In spite of the increase of the СаОw.s. content in the phosphorus concentrates the rising of the extent of removal of nitrate calcium is observed since the total mass of calcium nitrate is less in these phosphorus concentrates than in the phosphorus concentrates, obtained with a norm of НNО3 45 %. Fig. 2 shows the Са(NО3)2 concentration in the mixed liquid phases I and II as depending on the concentration of the repulping solutions of Са(NО3)2. It is seen, that with an increase of the concentration of repulping solutions of Са(NО3)2, its concentration is raised. From the data in Table 2 and Fig. 2 it is seen that the optimum concentration of repulping solutions of Са(NО3)2 is 10 % and ratio of PRM:solution of Са(NO3)2 = 1:2.5 at norm of HNO3 50 %. At that is obtained phosphorus concentrate containing (mass %): Р2О5t. 26.25; P2O5 ac.c.a. 11.88; P2O5 EDTA 7.99; СаОt. 39.81; СаОac.c.a. 18.50; СаОw.s. 1.86; ac. СО2 2.32; N 0.92; СаО: P2O5 1.52. The single drawback for the obtained phosphorus concentrate is the increased content of СаОw.s.- 1.86 %, in recalculation to Са(NО3)2 - 5.45 %. It was specified above that the content СаОw.s. not be more than 1.5 %, (in recalculation for Са(NO3)2 > 4.4). Therefore in our further research we studied the influence of the quantity and the temperature of the washing water which lead to a minimum of Са(NO3)2 content in the phosphorus concentrates. Influence of the quantity and temperature of the water on the quality parameters of phosphorus concentrates [12,13] In order to obtain a phosphorus concentrate with a minimal content of Са(NO3)2, we studied the influence quantity and temperature of water on the quality parameters of the phosphorus concentrates. The obtained data are presented by a volumetric graph (Fig. 3). It is seen that with increase of the ratio of PRM:solution of Са(NO3)2 from 1:2.0 to 1:3.0, the content of СаОw.s. is decreased notably in the phosphorus concentrates. The amount water contributes also to decreasing of the latter. The more is the water, the less is the content of СаОw.s. in phosphorus concentrates. Thus, with increasing of the amount of water, the calcium nitrate content will be reduced, i.e. the extent of removal of calcium nitrate from phosphorus concentrate is raised and the calcium 15 20 Extent of removal of Са(NO3)2 % CaO ac.c.a 11.59 11.87 11.55 11.88 11.15 11.33 11.09 11.27 CaOtotal 25.85 26.40 25.63 26.25 24.70 25.00 24.51 24.82 P2O5ac.EDTA 1:2.0 1:2.5 1:2.0 1:2.5 1:2.0 1:2.5 1:2.0 1:2.5 Norm of HNO3, 45 % 6.79 41.25 17.72 6.98 40.80 17.87 6.97 41.35 18.62 7.14 40.89 18.49 6.57 41.35 18.82 6.86 41.10 19.05 6.58 41.81 20.16 6.86 41.65 20.39 Norm of HNO3, 50 % 7.54 40.50 18.02 7.77 39.80 18.13 7.54 40.53 18.32 7.99 39.81 18.50 7.33 40.83 19.85 7.62 40.23 19.81 7.33 40.95 20.15 7.64 40.65 20.27 СаО: Р2О5 10 10.66 10.91 10.73 10.92 10.21 10.43 10.17 10.37 СО2t 5 24.55 24.81 24.35 24.67 23.15 23.53 23.02 23.34 Nt. 20 1:2.0 1:2.5 1:2.0 1:2.5 1:2.0 1:2.5 1:2.0 1:2.5 CaOw.s. 15 P2O5ac.c.a 10 P2O5t. 5 Ratio of PRM : solution of Са(NO3)2 Concentration solution of Са(NO3)2, % Table 2. Chemical composition phosphorus-concentrates. 2.26 1.66 2.37 1.75 2.59 2.27 3.01 2.67 1.12 0.82 1.18 0.87 1.25 1.21 1.35 1.29 2.70 2.63 2.64 2.50 2.45 2.32 2.41 2.27 1.68 1.64 1.70 1.66 1.79 1.75 1.82 1.78 91.65 94.10 91.34 93.71 89.23 90.92 87.27 89.03 2.40 1.70 2.52 1.86 2.84 2.51 3.15 2.96 1.19 0.86 1.25 0.92 1.32 1.24 1.52 1.33 2.49 2.36 2.45 2.32 2.31 2.19 2.18 2.10 1.57 1.51 1.58 1.52 1.65 1.61 1.67 1.64 92.75 94.93 92.00 94.41 90.21 91.66 89.02 90.01 31 Journal of Chemical Technology and Metallurgy, 50, 1, 2015 22 • 21.73 • 20.96 • 20.80 21 8 20.15• Concentration of Са(NO3)2 in mixes, % 20 00 00 19 00 000 00 18 00 • 2 • 20.15 • 19.47 19.60 18.89 • • 18.80 • 18.24 00 00 17 0 1 • • 17.45 17.19 2 1 15.96 16 16.84• • • 16.16 15.70 • 1 1 15 15 10 5 Concentration of repulping Са(NО3)2 solutions, % 20 Fig. 2. Change of the concentration of Са(NO3)2 depending on the concentration of the repulping solutions of Са(NО3)2. 1,11- norm of НNO3 45 % in ratio of PRM:solution of Са(NO3)2 = 1:2.0 and 1:2.5, respectively; 2,21- norm of НNO3 50 % in ratio of PRM:solution of Са(NO3)2 = 1:2.0 and 1:2.5, respectively. The content СаОw.s. in phosph.-concen., % 2.9 2.87 • 2.8 2 2.7 2.61 2.6 • 2.52 • 2.5 2.4 2.35 • 1.88• 1.9 • 2.3 2.37 1.8 •1.72 1.7 2.2 2.1 1.6 • 2.0 1.5 2,02 1.9 2.4 2.3 •2.25 1.71 2.2 • 1.62 • 2.1 •2.04 2.0 1.69 • • 1,62 1,7 1.6 •1.58 •1.52 1.5 1.9 1 1.8 1.8 1.7 1.7 1.6 1.6 1.5 1.5 1:3.0 1:2.5 PRM : solution of Са(NO3)2 1:2,0 1:1.0 1:1.5 1:2.0 PRM: Н2О Fig. 3. Dependence of the content of СаОw.s. in the phosphorus concentrates on the ratio PRM:Н2О and the ratio PRM:solution of Са(NO3)2. The norm of НNO3 is :1 - 45 %; 2 – 50 %. module will be decreased. It should be mentioned that at the above ratios of PRM:Н2О we could not fully separate the wet phosphorus concentrate from the calcium nitrate. Therefore, we should not increase higher the amount of water as with that, the water drain is diluted violently on calcium nitrate. On this basis we believe that at washing of the wet phosphorus concentrate it is necessary to control the 32 water amount. In our case the ratio PRM:Н2О = 1:1.5, at ratio of PRM:solution of Са(NO3)2 = 1: (2.5-3.0) is better since the by-product - solution of calcium nitrate will be obtained comparatively more concentrated. It is known that in washing of wet phosphorus concentrate besides the water amount, its temperature also has an important function. In addition, the solubility of the calcium nitrate in water depends considerably on temperature. Bokhodir E. Sultonov, Shafoat S. Namazov, Bakhtiyar S. Zakirov 1:2.0 1:2.5 24.86 25.24 11.17 11.39 1:2.0 1:2.5 25,15 25,77 11,32 11,65 1:2.0 1:2.5 25.63 26.25 11.55 11.88 1:2.0 1:2.5 25.89 26.75 11.68 12.12 1:2.0 1:2.5 26.23 27.04 11.85 12.26 1:2.0 1:2.5 26.28 27.10 11.89 12.28 1:2.0 1:2.5 26.33 27.14 11.90 12.30 For example, at 200С its solubility equals 128.8 g, at 300С - 149.4 g, at 400С - 189 g, at 600С - 359 g and at 1000С - 363 g [17]. Following these data the influence of washing water temperature on the quality of phosphorus concentrates was studied. The laboratory tests results are shown in Table 3. It is seen that with increasing washing water temperature from 20 to 800oС at ratio PRM: solution of Са(NO3)2 = 1:2.0, the content of P2O5t. increases from 24.86 tо 26.33 %, but the calcium module of the phosphorus concentrate is decreased from 1.69 tо 1.52, the extent of removal of Са(NO3)2 from the phosphorus concentrate changes from 89.34 tо 93.59 %. The contents of СаОt. and СаОw.s. go down from 41.89 to 40.05 % and from 3.05 tо 2.15 %, respectively. At ratio of PRM:Н2О = 1:2, increase of washing water temperature from 20 tо 800oС������������������������ to contributes to raising of the P2O5t. content from 25.24 tо 27.15 % in the samples of phosphorus concentrates, but the calcium module decreases from 1.61 tо 1.44. In addition, the extent of removal of Са(NO3)2 goes up from 92.51 tо 95.97 %, as well. СаО: Р2О5 Extent of removal of Са(NO3)2 % Тemperature of washing water = 200С 7.28 41.89 18.85 3.05 1.53 7.65 40,68 18.57 2.25 1.13 Тemperature of washing water = 300С 7.38 41.05 18.52 2.84 1.42 7.83 40.26 18.44 2.01 1.01 Тemperature of washing water = 400С 7.54 40,53 18,32 2,52 1,25 7.99 39,81 18,50 1,86 0,92 Тemperature of washing water = 500С 7.62 40.31 18.24 2.37 1.18 8.16 39.56 18.43 1.65 0.82 Тemperature of washing water = 600С 7.73 40.18 18.20 2.24 1.12 8.25 39.21 18.27 1.54 0.77 Тemperature of washing water = 700С 7.76 40.10 18,20 2.18 1,09 8.29 39.10 18.24 1.48 0.74 Тemperature of washing water = 800С 7.78 40.05 18.18 2.15 1.07 8.31 39.06 18.24 1.45 0.72 СО2t. Nt. CaOw.s. CaO ac.c.a CaOtotal P2O5ac.EDTA P2O5ac.c.a P2O5t. Ratio of PRM: solution of Са(NO3)2 Table 3. Chemical composition of the phosphorus concentrates. 2.39 2.31 1.69 1.61 89.34 92.51 2.42 2.34 1.63 1.56 90.54 93.65 2,45 2,32 1,58 1,52 92,00 94,41 2.47 2.36 1.56 1.48 92.66 95.24 2.48 2.38 1.53 1.45 93.26 95.68 2.48 2.39 1.52 1.44 93.47 95.88 2.48 2.39 1.52 1.44 93.59 95.97 The contents of СаОt. and СаОw.s. change from 40.68 tо 39.06 % and from 2.25 to 1.45 %, respectively. So, the quality of phosphorus concentrate is significantly improved. It should be noted that for temperatures of washing water above 600oС, independently of the ratio of PRM:solution of Са(NO3)2, the quality of the phosphorus concentrate is not changed. It is connected with an unimportant variation of the calcium nitrate solubility in the range of 60 - 800oС. When temperatures of washing water are lower than 500oС, a plentiful amount of Са(NO3)2 is precipitated. So, preferably the washing of the wet cake should be carried out at temperatures between 60oС and 70oС. CONCLUSIONS From the results obtained the following should be noted: ● The influence of nitric acid on the enrichment of phosphorite was studied and the pH of the medium was determined, at which the passage of P2O5 into liquid phase was excluded. ● The optimal concentration for the repulping solution of Са(NO3)2 was defined. 33 Journal of Chemical Technology and Metallurgy, 50, 1, 2015 ● The influence of the quantity and temperature of the washing water on the extent of removal of Са(NO3)2 from the phosphorus concentrate were studied. ● The possibility for obtaining of chemical phosphorus concentrate by interaction of phosphorite of Central Kyzylkum with nitric acid was shown. The chemical composition of the phosphorus concentrate is suitable for sulfur acid extraction for wet-processing of phosphoric acid and phosphorus-containing fertilizers on its base. 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