The Application of Advanced Materials on the Water or Wastewater TreatmentView this Special Issue
Research Article | Open Access
Feng-shan Zhou, Bo Hu, Bao-lin Cui, Feng-bao Liu, Fang Liu, Wei-heng Wang, Yang Liu, Rong-rong Lu, Ying-Mo Hu, Yi-he Zhang, Jin-Guang Wu, "Preparation and Characteristics of Polyaluminium Chloride by Utilizing Fluorine-Containing Waste Acidic Mother Liquid from Clay-Brine Synthetic Cryolite Process", Journal of Chemistry, vol. 2014, Article ID 274126, 7 pages, 2014. https://doi.org/10.1155/2014/274126
Preparation and Characteristics of Polyaluminium Chloride by Utilizing Fluorine-Containing Waste Acidic Mother Liquid from Clay-Brine Synthetic Cryolite Process
Clay-brine process employing activated clay, NaCl, HCl, and HF as raw materials is the primarily advanced technology to synthesize cryolite in the present industrial grade. However, plenty of byproducts of fluorine-containing waste HCl at the concentration of about 10%~12% could not be utilized comprehensively and are even hazardous to the environment. This work proposed a new two-step technology to prepare inorganic polymer flocculants polyaluminium chloride (PAC) from synthetic cryolite mother liquor. Many specific factors such as the variety of aluminide source, reaction temperature and time, reagent ratio, and manner of alkaline addition were taken into consideration and their influences on the performances of produced PAC were discussed. It was found that synthetic cryolite mother liquor could react with bauxite and calcium aluminate directly to prepare cheap PAC, with plenty amount of water insoluble CaF2 and CaSiF6 produced as well. However, once HCl was introduced into synthetic cryolite mother liquor as well as by utilizing bauxite as aluminide source and sodium aluminate as adjusting basicity agent, the resultant PAC would dissolve out higher amount of aluminum while producing little amount of water insoluble materials. The coagulation behavior of the specially produced PAC could even match the industrial grade PAC conforming to national standard.
1.1. Cryolite and Clay-Brine Synthetic Process
Cryolite, with professional name sodium aluminum fluoride and molecular formula Na3AlF6, is a kind of white and small-geometry crystal whose group can be divided into synthetic cryolite and natural cryolite according to the origin of the material itself. It is well recognized that synthetic cryolite possesses much higher solubility than natural cryolite. The other property parameters of synthetic cryolite are as follows: specific gravity 3, hardness 2~3, melting point 1000°C, and air-slaking after absorption of water. Due to these distinguished properties, cryolite has been applied in diverse fields, among which being utilized as fluxing agent is one of the most common ways. Besides, it is also the significant raw material of aluminium industry. For example, about 100~120 kg cryolite was reported to be consumed to produce 1 t metal-alumina in the present technology . Thus, it is concluded that the large-scale aluminium industry would never exist in this world without cryolite.
There are various kinds of process routes to fabricate cryolite in industry and the raw materials differ greatly from each other accordingly. Among all the technology routes, the most industrial competitive and representative one is the well-known clay-brine process (CBP) employing activated clay, NaCl, HCl, and HF as raw materials . The famous Do-fluoride Chemicals Co. Ltd. located in Jiaozuo of China is the biggest production corporation in the world to produce synthetic cryolite and the process route it adopts is also the CBP as shown in Figure 1.
1.2. Features of Cryolite Mother Liquor
Fluorine-containing waste hydrochloric acid from CBP of synthetic cryolite is also commonly known as synthetic cryolite mother liquor (SCML). According to the following CBP reaction principles , 6 mol affiliated HCl will be produced to fabricate 1 mol cryolite with AlCl3 as the aluminide source. The amount would even increase to as high as 12 mol once AlCl3 is replaced by Al2O3 as the aluminide source. Among the total 12 mol HCl, 6 mol HCl would reverse back into the system to leach the clay for cycling utilization. However, the other 6 mol HCl would still remain as residue in the system and need to let out for postprocessing, enhancing the complexity as well as the cost of the process route remarkably. It is estimated that 50 000 m3/a extra acidic synthetic cryolite mother liquor would be created if Do-fluoride Chemicals Co. fabricates 20 000 t/a synthetic cryolite [3–5]. Consider
Though SCML from CBP of synthetic cryolite possesses complicated composition as shown in Table 1, F−, Cl−, H+, and Na+ are four main kinds of ions in it. Meanwhile, the total acidity ranges from 110 g/L to 140 g/L (or 3~4 mol/L) (or 10.4%~13.8%) and the weight percentage of NaCl is no more than 40 g/L. This is because the clay utilized in acid leaching is always made from the low grade calcined bauxite with and .
According to the standard of public water established by the American Environmental Protection Administration (EPA), drinking water with 0.4~0.6 mg/L F− will do benefit to human health. However, the situation is not that optimistic when drinking water with F− concentration higher than 1.0 mg/L for a long time which may even cause serious diseases such as dental and bone fluorosis . In addition, both the difficult controlling of technology and the expensive cost of waste outlet during the treatment process of SCML as acidic waste make corporations suffer from tremendous environmental protection pressure . And the enterprise has a great amount of waste acid liquid containing F−, which is badly in need of finding an environmental economy processing method. Meanwhile, it is difficult to polymerize in the preparation of PAC because of the common ion effect of F−. We need to search for a new preparation method in this paper. Thus, this work optimized the process route using SCML to produce inorganic polymer flocculants (IPFs) polyaluminium chloride (PAC). Moreover, the reason for the generation of highly water insoluble materials was well explained via exploration of the XRD phase of products from the reactions. Besides, the well cost performance product PAC was obtained and the optimized route had also been applied in industry.
2. Materials and Experimental Methods
2.1. Materials and Instruments
Sodium aluminate, HCl, HAc, NaAc, Zn(Ac)2, NH3·H2O, KF, and EDTA were used for chemical purity. Other purchased industrial grade raw materials included technical hydrochloric acid diluted to 18 wt%; bauxite (Al2O3 30 wt%); calcined bauxite (Al2O3 40 wt%); calcium aluminate powder (Al2O3 53 wt%, CaO 28 wt%); polyaluminium chloride (PAC, Al2O3 29 wt%). SCML was the byproduct acid from Do-fluoride Chemicals Co. and the composition was described in Table 1.
pH values were determined by pH500 meter, CLEAN, USA; SGZ-2 turbidimeter was employed to measure turbidity by Shanghai Yuefeng Instruments & Meters Co., Ltd; CODCr (potassium dichromate as oxidant) was measured by 5B-6 COD reactor, Lian-Hua Tech. Co., China.
2.2. Experimental Methods and Details
2.2.1. Preparation of PAC from Synthetic Cryolite Mother Liquor
Certain amount of synthetic cryolite mother liquor was added into a three-neck flask with a condenser firstly. After the temperature of the flask was heated to 70°C in oil bath, certain amount of bauxite was added into the system step by step. The reaction should continue for 1 h after the temperature increases to 100°C. Then alkaline polymerization adjusting agent (APA, calcium aluminate powder, or sodium aluminate powder) was added into the above reaction system gradually to adjust pH value. The addition speed of APA depended on pH value of the system: when pH value was lower than 2.7, the speed can be fast, but when it was over 2.7, the speed should be slow until it increased to 3.5~3.8 further. At this point, APA should not be added into the system any more. After all these operations, the reaction is kept for another 1.5 h at 100°C. Then the reaction should be suspended immediately via halting both the vigorous stirring and oil bath heating followed by coagulating the system for 12 h using the residual heat of oil bath. Liquid PAC was obtained after the filtering of the upper clear liquid of the already stewed reaction suspension. And solid PAC was finally obtained after the initial liquid PAC was dried at 105°C.
2.2.2. Basicity of the Produced PAC
OH− is the basic component influencing the morphology of polyaluminium chloride [6–9] whose index in PAC is measured by basicity (B). According to GB 15892-2003 (water treatment chemical-polyaluminium chloride) , basicity can be measured. The mol percentage of OH and Al in PAC is defined as basicity and this parameter can reflect the degree of polymerization of PAC to some extent, which affects the coagulation performances of PAC. Basicity can be calculated according to the following during the fabrication process of PAC:
2.2.3. Coagulation Performance of the Produced PAC
Coagulation tests were performed by using simulated diatomite water and real oily wastewater samples. All coagulation tests were conducted in 100 mL beakers using a magnetic stirring apparatus. 100 mL of the test water was placed in a beaker and stirred rapidly at 200 rpm for 2 min after adding the coagulant at room temperature, followed by slow stirring at 40 rpm for 2 min and sedimentation for 10 min. Then a supernatant sample was taken at 1.0 cm below the surface of the test water for turbidity and CODCr measurement.
2.2.4. Characterization of the Produced PAC
The produced PAC solution was dehydrated at 105°C and made powder sample for structure analysis. X-ray diffraction (XRD) was measured for the determination of crystalline phases in solid coagulants using D/max-rA X-ray diffractometer with Cu K radiation in the range of 3° to 80° at a scan rate of 8°/min. The solid produced PAC was analyzed by FT-IR with the Perkin Elmer spectrum 100 FT-IR spectrophotometer and potassium bromide pellet method. The spectra were scanned in the range of 4000 to 500 cm−1.
3. Results and Discussion
3.1. Synthesis Optimization
The pH value of the leaching reaction system was the most critical technological parameter during the fabrication process of PAC [11–13]. Due to the amphoteric compound property of aluminum, the state of aluminum salt solution showed certain transformation law along with pH value alteration. When the pH value of the leaching agent was less than 4, aluminum mostly existed as hydrated ions. These hydrated ions would get hydrolysed as pH value increased, and the mononuclear or monohydroxy compounds would first generate, and then the new produced compounds evolve into three-nuclear or multi-hydroxy compounds along with further increase of pH value. In this compound, bridging effect took place between ions and hydroxyl, creating multiple nuclear hydroxyl complexes known as inorganic polymer. The specific states of aluminum salt solution along with pH value alteration were as follows [13–15]: , , n = 6~10; , , , , ; , ; , , .
The chemical equations to prepare PAC were indicated as follows:
According to the above reaction principles, the influencing factors such as the kind and amount of APA, amount of water insoluble material, and leaching aluminum as well as the degree of polymerization (or basicity) were deeply discussed in this work and results were described in Table 2 from which two laws were concluded.(1)Once synthetic cryolite mother liquor was the only taken acid leaching agent, the leaching efficiency of aluminum was not that high. Nevertheless, it could be enhanced apparently when appropriate HCl was added into synthetic cryolite mother liquor.(2)When calcium aluminate was used as APA, Ca2+ would react with F− and in synthetic cryolite mother liquor and high amount of water insoluble material was thus produced. However, if calcium aluminate was replaced by sodium aluminate as APA, the amount of water insoluble material would decrease significantly.
Based on the above experimental results, the reaction condition was optimized as follows: 200 mL mixed acid was obtained first by blending 150 mL synthetic cryolite mother liquor (containing HCl 12%) with 50 mL industrial 31% concentrated HCl. 80 g bauxite was then added into the mix and the reaction was kept for 1~2 h at 80~100°C. The polymerization was completed when 23 g sodium aluminate was added into the system to adjust pH value followed by coagulation for 12 h under vigorous stirring. PAC with industrial quality standard could be obtained after the stewing and filtering of the reaction agent.
3.2. Structure of the Produced PAC
The final product following the optimized preparative conditions was analyzed with XRD and FT-IR to obtain detailed structural information.
XRD spectra of PAC (Sample B) generated from polymerization induced by calcium aluminate as pH adjusting agent were showed in Figure 2. It was indicated that there appeared characteristic absorption bands assigned to water insoluble CaF2 and CaSiF6 besides the absorption band of AlCl3. This might be because HF in synthetic cryolite mother liquor dissolved SiO2 in calcium aluminate into and both and F− encountered Ca2+ leached from calcium aluminate to form water insoluble CaF2 and CaSiF6.
However, in the XRD spectra of PAC (Sample C) generated from polymerization induced by sodium aluminate as pH adjusting agent (Figure 3), it was not difficult to find that there existed characteristic absorption bands of Fe except for the absorption band of AlCl3. This might be because HF and HCl in synthetic cryolite mother liquor dissolved Fe in bauxite into Fe2+ and Fe3+, with Fe(OH)3 further produced.
In order to confirm that Fe in bauxite can be abundantly dissolved out in acid leaching process, SCML and HCl mixed acid was proposed to leach bauxite. XRD results of the crystal obtained from the dried leaching solution indicated that the main components of this crystal contained SiF4, AlCl3·6H2O, and Na2Al22O34 (Figure 4). Thus, it was clear that PAC prepared from SCML was rather different from industrial grade PAC. Instead, it was made up of multiple crystal phases and components and AlCl3, FeCl3, SiF4, and H2SiO3 were especially typical. The plural gel formed by the polymerization of these components might show synergism effect on the coagulation characteristic of PAC [16–20].
It was well recognized in collochemistry that the positive discharged Fe(OH)3 colloidal particles with small amount in system could create bridged bonds among negative colloidal particles just like coagulating agent, thus getting precipitated via mutual absorption. On this occasion, Fe(OH)3 functioned as coagulant aid [18, 19].
The existence of small amount of silica sol (also ludox) not only could promote the coagulating process of water as well as improving the structure of precipitation particles, but also could increase their weight, accelerating the formation and precipitation of precipitation particles. Therefore, silica sol could also function as coagulant aid. Unlike the large amount of positive charge of Al13 as key component of flocculation agent of PAC, the surface of silica gel particles was filled with negative charge instead. Thus, these two kinds of particles with totally opposite charge would allure each other to get absorbed. Meanwhile, silica gel could also absorb other scattered colloidal particles with positive charge, strengthening the coagulating effect accordingly [15, 17, 21, 22].
From the above discussion, it was found that the produced PAC by SCML (PAC-SCML) was rather different from common industrial grade PAC (PAC-IG). Except for the relative strong coagulating character, it was a kind of composite flocculant containing certain amount of Fe and Si, which could be treated as the compound of PAC, polyaluminum ferric chloride (PAFC), and polysilicate (PSi) [18–20, 23]. Besides, FT-IR spectra of this special PAC showed much difference from that of common PAC as indicated in Figure 5.
The possible chemical bonds in PAC-SCML (Sample C) were investigated by the FT-IR spectra and were compared with PAC-IG (Figure 5). The two samples showed similar FT-IR spectra. Both spectra exhibited a broad absorption peak in the range of 3200–3650 cm−1 (3390 cm−1 for PAC-SCML and 3430 cm−1 for PAC-IG), which could be assigned to the stretching vibrations of –OH groups. The peaks in the range of 1600–1700 cm−1 (1628 cm−1 for PAC-SCML and 1636 cm−1 PAC-IG) were attributed to the bending vibrations of water absorbed, polymerized, and crystallized in the coagulant. The PAC-IG was not a pure substance, which also contains some iron ions. The peak at 1098 cm−1 for PAC-SCML and the peak at 1090 cm−1 for PAC-IG were attributed to the asymmetric stretching vibration of Fe–OH–Fe or Al–OH–Al; furthermore, there were two peaks at 778 cm−1 and 640 cm−1 for PAC-SCML and two peaks at 770 cm−1 and 578 cm−1 for PAC-IG, which were attributed to bending vibrations of Fe–OH and Al–OH, respectively [24–28].
3.3. Coagulation Characteristics
Coagulation tests were performed by using simulated diatomite water and real oily wastewater samples. The turbidity of the simulated diatomite water samples was 1480 NTU, 720 NTU, and 80 NTU. The CODCr of the oily wastewater samples obtained from Liaohe Petroleum Exploration Bureau of China was 534 mg/L and its turbidity was 124 NTU.
As indicated in the flocculation results in Table 3, the coagulation effect of PAC-IG was much better than that of PAC-SCML for simulated diatomite water with low turbidity. However, the coagulation effect of PAC-SCML had distinguished advantages over that of PAC-IG for simulated diatomite water with high turbidity, which might originate from the formation of PAFC and PSi with strengthening coagulation effect in acid leaching process. Moreover, the small amount of water insoluble CaF2 and CaSiF6 in PAC-SCML could also benefit the coagulating reaction for high turbidity water.
The CODCr removal of PAC-SCML and PAC-IG both achieved the minimum at 60 mg/L dosage while PAC-SCML was relatively superior to PAC-IG for oily sewage from Liaohe Oilfield, and the same law was presented for turbidity removal.
The results suggested that despite the small difference in alumina content between PAC-SCML and PAC-IG, PAC-SCML was superior to PAC-IG in both the comprehensive coagulating character and manufacturing cost due to the certain amount of Fe and Si in PAC-SCML.
The preparation of PAC coagulant from synthetic cryolite mother liquor from clay-brine process (PAC-SCML) with advanced performances compared with conventional industrial grade PAC (PAC-IG) coagulant was achieved. Reaction conditions including the choice of leaching acid and alkaline polymerization adjusting agent, the pH value, and the reaction temperature and reaction time were thoroughly studied to optimize the coagulation performances and minimize the insoluble solid in water of the prepared coagulant. The optimized technique to prepare PAC-SCML was that adjusting the concentration of HCl in synthetic cryolite mother liquor to 18% with the industrial grade HCl (the concentration about 32% to 36% in general) firstly, and then adding the needed bauxite. Then the acid leaching reaction was kept for 1~2 h at 80~100°C and sodium aluminate was consequently added to adjust pH value to 3.5~3.8. The whole technology would be completed after a 24 h coagulation process. The coagulation performances tested showed that PAC-SCML is better than PAC-IG in turbidity removal at high turbidity simulated diatomite water and in CODCr removal at real oily wastewater. Both XRD and FT-IR results confirmed that there existed certain amount of Fe and Si in PAC-SCML, which could combine Al to form multiple nuclear inorganic polymer and make the resultant PAC-SCML possess advanced coagulating performances. This technology will become an effective way to treat the large amount of waste acid solution in cryolite fabrication process.
Conflict of Interests
The authors declare that there is no conflict of interests regarding the publication of this paper.
This research was supported by the National High Technology Research and Development Program (863 Program 2012AA06A109) of China.
- H. P. Ding, “Production technology and market situation of cryolite products,” Yunnan Metallurgy, vol. 33, no. 3, pp. 64–69, 2004.
- Z. Y. Tang, “Producing sand like synthetic cryolite by clay bittern method,” Patent CN 1056091 A, 1991.
- H. H. Yu, H. Wang, S. Y. Yang et al., “The comprehensive utilization of aluminium fluoride mother liquor,” Inorganic Chemicals Industry, vol. 37, no. 4, pp. 34–35, 2005.
- T. Dong, J. M. Liu, Z. X. Li et al., “High concentration fluoride wastewater treatment,” Tianjin Chemical Industry, vol. 18, no. 5, pp. 58–60, 2004.
- M. Zhang, H. N. Yang, X. X. Zhang et al., “Preparation of polyaluminium ferrous chloride by using cryolite mother liquor,” Inorganic Chemicals Industry, vol. 42, no. 3, pp. 43–44, 2010.
- L. Allouche and F. Taulelle, “Conversion of Al13 Keggin ε into Al30: a reaction controlled by aluminum monomers,” Inorganic Chemistry Communications, vol. 6, no. 9, pp. 1167–1170, 2003.
- W. Seichter, H. J. Mogel, P. Brand, and D. Salah, “Crystal structure and formation of the aluminium hydroxide chloride Al-13(OH)(24)(H2O)(24) Cl-15 center dot 13H(2)O,” European Journal of Inorganic Chemistry, no. 6, pp. 795–797, 1998.
- W. Z. Wang and P. H. Hsu, “The nature of polynuclear OH-Al complexes in laboratory-hydrolyzed and commercial hydroxyaluminum solutions,” Clays & Clay Minerals, vol. 42, no. 3, pp. 356–368, 1994.
- J. E. van Benschoten and J. K. Edzwald, “Chemical aspects of coagulation using aluminum salts—I. Hydrolytic reactions of alum and polyaluminum chloride,” Water Research, vol. 24, no. 12, pp. 1519–1526, 1990.
- GB15892-2003, “Water treatment chemical-Poly aluminium chlorid. Chinese administration of quality supervision, inspection and quarantine”.
- R. R. Lu, Y. H. Zhang, F. S. Zhou, X. Wang, Q. An, and Z. Meng, “Novel polyaluminum ferric chloride composite coagulant from Bayer red mud for wastewater treatment,” Desalination and Water Treatment, vol. 295, pp. 1–9, 2013.
- W. Li, T. Hua, and Q. X. Zhou, “Preparation, morphology and coagulation characteristics of a new polyferric chloride coagulant prepared using pyrite cinders,” Environmental Technology, vol. 32, no. 8, pp. 911–920, 2011.
- Z. L. Huang, Y. H. Hu, and Z. F. Jiang, “Preparation of polyaluminum chloride from waste chlorhydric acid and poor quality Kaolin,” Environmental Protection of Chemical Industry, vol. 22, no. 5, pp. 284–286, 2002.
- W. Lan, H. Qiu, J. Zhang et al., “Characteristic of a novel composite inorganic polymer coagulant-PFAC prepared by hydrochloric pickle liquor,” Journal of Hazardous Materials, vol. 162, no. 1, pp. 174–179, 2009.
- T. Sun, C. Sun, G. Zhu et al., “Preparation and coagulation performance of poly-ferric-aluminum-silicate-sulfate from fly ash,” Desalination, vol. 268, no. 1–3, pp. 270–275, 2011.
- G. Zhu, H. Zheng, W. Chen, W. Fan, P. Zhang, and T. Tshukudu, “Preparation of a composite coagulant: polymeric aluminum ferric sulfate (PAFS) for wastewater treatment,” Desalination, vol. 285, no. 31, pp. 315–323, 2012.
- B. Y. Gao, Z. S. Wang, and H. X. Tang, “Study on the hydrolysis-polymerization process of aluminum and the interaction between hydrolyzed aluminum species and polysilicic acid in flocculant polyaluminum silicate chloride (PASC),” ACTA Scientiae Circumstantiae, vol. 20, no. 2, pp. 151–153, 2000.
- F. S. Zhou, L. Ma, J. G. Wu et al., “Complexing agent, preparing method and use thereof,” CN1552629, 2004.
- F. S. Zhou, L. Ma, J. G. Wu et al., “Complexometric synergist, preparing method and use thereof,” CN1552636, 2004.
- F. S. Zhou, L. Ma, J. G. Wu et al., Flocculent, preparing method and use thereof. CN1552637, 2004.
- D. S. Wang and H. X. Tang, “Poly ferric silicon type compound inorganic high molecular flocculant and its preparing method,” CN1210818, 1999.
- Z. P. Ai, B. Y. Gao, and S. R. Wang, “Electron microscopic observation on sol and gel of polysilicic acid,” Environmental Chemistry, vol. 13, no. 2, pp. 119–122, 1994.
- Y. M. Fang, X. D. Zhao, and X. L. Zhang, “Study on the image, structure and coagulation behavior of polysilicate-aluminum ferric,” Industrial Safety and Environmental Protection, vol. 33, no. 10, pp. 22–24, 2007.
- F. Zhou, S. Wang, J. Su et al., “Structural characteristics of infrared spectra for polyaluminum chloride in enhanced reactions of modification,” Spectroscopy and Spectral Analysis, vol. 24, no. 5, pp. 532–535, 2004.
- H. Yu, B. Y. Gao, Q. Y. Yue et al., “Study on the structural characteristics of polyaluminum silicata chloride by infraed spectrum method,” Journal of Shandong University (Natural Science Edition), vol. 34, no. 2, pp. 198–201, 1999.
- W. N. Chen, H. P. Zhong, J. Yang et al., “Analysis of IR spectrum and crystal morphology of polyalumina-silica chlorid (PASC) prepared by various method,” Chemical Research and Application, vol. 14, no. 1, pp. 73–75, 2002.
- F. S. Zhou, S. H. Wang, J. Z. Su et al., “Infrared spectra and characteristics of PMC—a multicore inorganic polymer flocculant,” Fine Chemicals, vol. 20, no. 10, pp. 615–618, 2003.
- X. Zhang, L. Zhou, and M. Tang, “Study of infrared spectra of polyaluminum ferric chloride,” Spectroscopy and Spectral Analysis, vol. 22, no. 1, pp. 39–42, 2002.
Copyright © 2014 Feng-shan Zhou et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.