M E C H A N I C A L PA P E R S Calcium ion removal by a synthetic zeolite in the manufacture of mechanical grade papers By J.-B. Thibodeau, B. Chabot and C. Daneault Abstract: The removal of free calcium ions from paper machine white-water by a synthetic zeolite (type 4A) was examined. We have studied the effect of various parameters and operating conditions. Results showed that zeolite 4A is very efficient at removing free calcium ions from whitewater. Conductivity, reaction time, temperature, fibre content and wood extractives concentration have no significant detrimental effect on calcium ion removal by the zeolite. ALCIUM CARBONATE fillers (PCC and GCC) are still not widely used in wood-containing papers in North America. Two limitations are associated with their use. First, the high alkalinity of the calcium carbonate slurry reduces the brightness of mechanical pulp [1]. Second, the pH strongly influences the solubility of calcium carbonate filler [2,3]. Paper machines traditionally operate under acidic pH. Under these conditions, calcium carbonate is attacked by acids releasing free calcium ions and carbon dioxide in white-water systems [4]. Free calcium ions can then react with dissolved and colloidal substances (DCS), promoting the formation of deposits that can affect paper machine operation and reduce paper quality [5]. Inhibition of calcium carbonate dissolution has been studied for several years. Compton et al [6,7] determined the effect of specific chemicals at inhibiting calcium carbonate dissolution. An acid tolerant precipitated calcium carbonate (ATPCC) has recently been developed for use as a filler in wood-containing paper manufacturing [8]. This technology is based on a buffer effect between a conjugated base (sodium hexametaphosphate) and a weak acid (phosphoric acid). Addition of carbon dioxide gas to the pulp slurry has also been tried to retard dissolution of calcium carbonate filler [9,10]. Both technologies are currently used in some mechanical paper mills in Europe, but their acceptance is still limited in North America. White-water management around the paper machine and TMP pulp mill must also be considered when dealing with calcium carbonate fillers. Large volumes of excess white-water from the paper machine are used at the TMP plant for dilution purposes and refiners operations. Acidic conditions prevailing at the TMP plant will completely dissolve calcium carbonate filler carried over with dilution white-water. This problem can be limited by using a properly operating disk filter to recover solid calcium carbonate filler as much as possible. Otherwise, calcium carbonate filler will be transferred into the cloudy filtrate, to the paper machine white-water chest, and eventually to the TMP plant. Complete separation of white-water systems for the paper machine and C J.-B. THIBODEAU Centre de recherche en pâtes et papiers, UQTR, Trois-Rivières, QC B. CHABOT Centre de recherche en pâtes et papiers, UQTR, Trois-Rivières, QC [email protected] C. DANEAULT Centre de recherche en pâtes et papiers, UQTR, Trois-Rivières, QC 42 ❘❘❘ 106:3 (2005) the pulp mill could also be considered. Zeolites are three-dimensional networks of silicate and aluminate tetrahedra linked together by shared oxygen atoms. Their structure is a framework that encloses cavities occupied by cations weakly held to the structure to compensate for the charge imbalance created by the substitution of Al3+ for Si4+ in the tetrahedral structure. They have pore structures with interconnecting channels large enough for ions to enter in the cavities without disrupting the network. The type 4A zeolite is a sodium-form zeolite, used successfully in the laundry detergents industry as a builder to improve detergent efficiency in hard water due to its great capacity for calcium-ion exchange [11]. Zeolites are also used for softening drinking water [12]. Studies have also shown the effectiveness of zeolites to remove heavy metal ions from wastewaters [13-16]. We have recently studied the potentials of zeolite 4A in the manufacture of supercalendered papers [17]. This work was mainly focusing on the use of zeolites as a substitute to traditional fillers and their potential effects on retention, drainage and sheet properties. However, preliminary results in simulated white-water systems have shown high calcium-ion exchange ability. The objective of this paper is, thus, to further investigate the effect of several parameters on the calcium-ion exchange capacity of a synthetic zeolite (type 4A) under papermaking conditions. EXPERIMENTAL Materials: The zeolite (Valfor 100) was supplied by PQ Corporation. It is a sodium aluminosilicate hydrated type Na-A zeolite. The nominal pore size diameter is 4 Angstroms (Type 4A). According to the supplier, the ion exchange and calcium exchange capacities are 7 meq/g anhydrous zeolite and 270-300 mg CaCO3/g zeolite (anhydrous basis), respectively [17]. Table I shows other important properties of the zeolite studied [18]. A commercial calcium carbonate (GCC) slurry was supplied by Omya. The solid content was 65%. Unbleached thermomechanical pulp (TMP) was sampled at an Eastern Canadian paper mill. Pulp properties are shown in Table II. White-waters were prepared by diluting an appropriate amount of TMP pulp to a consisten- T 71 Pulp & Paper Canada M E C H A N I C A L PA P E R S Table I. Properties of zeolite 4a. Solids Active Composition (Dehydrated, mol%) Molar ratio (%) (%) Al Si Na Ca,K Al:Si 77.9 100 14.4 13.1 17.2 0.6 1.1 Table II. Unbleached TMP pulp properties. CSF (mL) Ash (%) Fines (%) Fibre length* (mm) Brightness (%) 88 1.41 59.8 0.34 63.0 *Average Table III. Disk filter white-water samples properties. Sample Consistency Ash CaCO3 (%) (%) (mg/L) Cloudy Filtrate Clear Filtrate Rich WW 4.57 3.06 7.45 150 160 130 0.053 0.037 0.253 FIG. 2. Effect of conductivity on the calcium-ion exchange ability of zeolite 4A in white-water. cy of 0.2% with tap water to simulate paper machine white-water. Dissolved and colloidal substances (DCS) were extracted from black spruce chips by steaming for 20 minutes in a pressurized vessel. After steaming, the condensate containing wood extractives was collected. For several experiments, a known amount of extractives was added to the white-water sample to determine the effect of DCS on calcium ion removal by the zeolite. White-water samples from a paper machine disk filter were also collected at the same paper mill. Table III shows their properties. The zeolite efficiency was determined directly in those samples. Calcium ion Removal by Zeolite: Figure 1 shows the experimental set-up for calcium ion removal by the zeolite 4A. Experiments were carried out at 50°C to simulate a typical papermaking temperature. Several experiments were also done at 25°C to study the effect of temperature. The following sequence was used for all experiments. First, a preheated white-water sample (500 mL) was Pulp & Paper Canada T 72 FIG. 1. Experimental set-up for calcium ion removal by zeolite. FIG. 3. Effect of temperature on the calcium-ion exchange ability of zeolite 4A in white-water. poured in a beaker. The beaker was then fitted in the temperature-controlled bath. The stirrer was set at 500 rpm to ensure proper agitation. Then, a predetermined amount of GCC was added to the system. The amount was determined to set the concentration at 200 ppm (or 1,000 ppm in few trials) (as CaCO3) in the beaker. The slurry was then adjusted to pH 5 using diluted hydrochloric acid to completely dissolve GCC filler into free calcium ions. Then, zeolite 4A was added to the slurry and mixing was allowed for 5 minutes at 500 rpm. Zeolite dosages were varied from 0 to 1 g/L (up to 5 g/L in several experiments). The pH, conductivity and temperature were recorded after all steps. After the mixing stage, a sample of the slurry was filtered on a 0.8-µm microporous membrane filter. The filtrate was saved for free calcium ion concentration determination by EDTA titration using hydroxynaphtol blue indicator. Calcium ion concentrations were reported as CaCO3. Experiments were repeated three times to determine the experimental error. RESULTS, DISCUSSION Effects of Conductivity, Temperature, and pH: Figure 2 shows the effect of conductivity on calcium-ion removal by the zeolite 4A. Conductivity was varied by adding sodium chloride in the white-water system. Free calcium ion concentration is decreasing with zeolite dosage at all conductivity level studied. It is clear that the residual free calcium ion concentration is dependent on zeolite dosages. This is attributed to the ion exchange capacity of zeolite 4A. However, the zeolite efficiency is slightly reduced as conductivity is increased. The curve at high conductivity (2,630 µS/cm) is slightly offset compared to others curves. This can be attributed to the higher starting calcium carbonate concentration used in this series of experiments. The effect of conductivity on zeolite exchange ability can be attributed to the higher osmotic pressure developed in the water phase when sodium ion concentration is increased. This higher osmotic pressure reduces the ability of sodium ion to get out of the zeolite cage, 106:3 (2005) ❘❘❘ 43 M E C H A N I C A L PA P E R S FIG. 4. Effect of suspension pH on the calcium-ion exchange ability of zeolite 4A in white-water. FIG. 5. Effect of contact time on calcium-zeolite stability. Experiments were carried out without pH control. FIG. 6. Effect of contact time on calcium-zeolite stability for a white-water system. Experiments were carried out at pH 5. thus reducing the over-all calcium ion uptake. Therefore, the ability of the zeolite 4A will be reduced at high conductivity levels although the efficiency is still very high. Figure 3 shows the effect of temperature on the zeolite performance. Increasing the temperature from 25°C to 50°C resulted in a slight improvement of the zeolite performance at removing free calcium ions from the white-water system. The gap between the two curves increases with zeolite dosage up to 0.5 g/L, and then should remain constant within the experimental error. Brouillette et al have recently shown that an increase in the temperature promotes dissociation of the surface hydroxyl groups of the zeolite surface resulting in a higher anionic charge [19]. A higher temperature also increases calcium ion dehydration resulting in a smaller ion size. Therefore, calcium ions can more easily enter inside the zeolite structure improving the over-all calcium ion uptake by the zeolite 4A. The effect of suspension pH on calcium uptake was also determined, Fig. 4. Two important phenomena must be considered. First, the zeolite is removing the free calcium ion in the white-water system at all pH studied. Second, the concentration of free calcium ion in the slurry is lower at higher pH as it is clearly demon- 44 ❘❘❘ 106:3 (2005) strated when no zeolite is added in the system. The large variation of the free calcium content is due to the solubility of GCC filler, which is strongly dependent on the suspension pH [1-3]. As the pH is decreased to lower pH values (from 7 to 4), the higher the concentration of free calcium ions available for exchange by the zeolite. Although the efficiency of zeolite seems to be lower at neutral pH, lower zeolite dosages will be required to reduce free calcium ion concentration under 100 mg/L which is considered acceptable levels in white-water systems. The properties of the calcium-zeolite aggregates could also be affected by the white-water suspension pH. Brouillette et al have shown that the zeolite is attacked at lower pH values (in the range of 3 to 4) [19]. This was shown to induce a certain dissolution of the zeolite framework. Therefore, it was necessary to evaluate the effect of contact time under acidic conditions to determine if already exchanged calcium ions could be released in the system after long contact time under these acidic detrimental conditions. Figures 5 and 6 show the effect of contact time on calcium ion uptake, pH and conductivity of the white-water suspensions. The zeolite dosage was adjusted at 0.5 g/L in both experiments. Figure 5 shows that the suspension pH was increased from 5 to 7.6 with contact time, while free calcium content remained constant at about 65 mg/L. This increase of the pH can be attributed to the adsorption of hydroxyl ions on the negative sites of the zeolite during the experiment and to a partial hydrolysis of the zeolite structure [20]. We did the same experiment but the pH was kept at 5 (the initial starting value) using a pH controller (see Fig. 6). In this case, the free calcium ion concentration slightly increased with time from about 95 mg/L to 105 mg/L, indicating that free calcium ions were released in the white-water during the experiment. Although the amount released was very low, this showed that acidic conditions did not destroy the zeolite structure during contact time (up to one hour). Therefore, it is believed that paper machine whitewater containing calcium-zeolite particles could be used safely at the TMP mill without any significant calcium ion loss during pulp processing. Effect of Contaminants in the White-Water System: Experiments were also performed to determine if contaminants carried over with process white-water could affect the efficiency of zeolite 4A at removing free calcium ions. Figure 7 shows the effect of added dissolved and colloidal substances (DCS) in the system on calcium ion removal by the zeolite 4A. DCS were added directly to the white-water system. Results indicate that DCS added to the system have no significant effect on the performance of the zeolite studied. To further investigate the possible detrimental effect of DCS on the efficiency of zeolite 4A, we also carried out experiments using paper machine white-water samples. Samples were collected from a disk filter (rich, cloudy, clear filtrates). Results are shown in Fig. 8. No significant detrimental effects were observed. This indicates that the zeolite 4A is not affected by DCS and fines contents. These also show that our proposed process is very robust and can be applied anywhere in the paper machine water loops to control calcium ion concentration. T 73 Pulp & Paper Canada M E C H A N I C A L PA P E R S FIG. 7. Effect of dissolved and colloidal substances concentration on the calcium-ion exchange ability of zeolite 4A. CONCLUSIONS • This study revealed that the zeolite 4A has a high calcium-ion exchange capacity in white-water systems prepared under various conditions. • Conductivity had no significant detrimental effect on calcium ion uptake. • Higher temperature slightly improved the zeolite performance at all dosages studied. • The efficiency of the zeolite was dependent on the calcium ion concentration, which is also strongly related to the suspension pH. • Addition of dissolved and colloidal substances (DCS) had no effect on zeolite efficiency. • Trials using paper machine white-waters sampled from a disk filter also showed no detrimental effect of calcium ion uptake. • The zeolite 4A can, thus, be used anywhere in the paper machine white-water loops to control the calcium ion level. ACKNOWLEDGEMENTS The authors gratefully acknowledge the Natural Sciences and Engineering Research Council of Canada (NSERC) for their financial support. Thanks are also offered to Omya Inc. (GCC), PQ Corporation (Zeolite 4A) and Kruger Trois-Rivières (pulps) for providing samples required for this work. LITERATURE 1. EVANS, D.B., DRUMMOND, D.K., KOPPELMAN, M.H. PCC Fillers for Groundwood Papers. Proc., TAPPI Papermakers Conf., Seattle, 321-330 (1991). 2. LAUFMANN, M., HUMMEL, W. Neutral Manufacture of Groundwood-Containing papers in the Nineties. Proc., TAPPI Papermakers Conf., Seattle, 299-320 (1991). 3. PHIPPS, J., LORUSSO, M. Dissolution Behaviour of Pulp & Paper Canada T 74 FIG. 8. Effect of white-water quality on the calcium-ion exchange ability of zeolite 4A. Calcium Carbonate in Mildly Acidic Conditions. Proc., 12th Fund. Res. Symposium, The Pulp and Paper Fundamental Research Society, Oxford, UK, 415-427, 1721 Sept. (2001). 4. AIN, R.L., LALEG, M. Mill Experiences with AT Precipitated Calcium Carbonate (PCC) in Papers Containing Mechanical Pulp. Pulp Paper Can. 98(12):172176 (December 1997). 5. ALLEN, L.H. The Importance of pH in Controlling Metal-Soap Deposition. Tappi J. 71(1):61-64 (1988). 6. COMPTON, R.G., BROWN, C.A. The Inhibition of Calcite Dissolution/Precipitation: Mg2+ Cations. J. Colloid Interface Sc. 165: 445-449 (1994). 7. COMPTON, R.G., BROWN, C.A. The Inhibition of Calcite Dissolution/Precipitation: 1,2-Dicarboxylic acids. J. Colloid Interface Sc. 170: 586-590 (1995). 8. PASSARETTI, J.D. Acid-Stabilized Calcium Carbonate, Process for its Production and Method for its Use in the Manufacture of Acidic Paper. US Patent 5156719, 20 October (1992). 9. LAURILA-LUMME, A., PAKARINEN, H., LEINO, H.J. Improved Papermaking Processes. PCT International Patent WO 99/45202, 10 September (1999). 10. PAKARINEN, H., LEINO, H. Benefits of Using Carbon Dioxide in the Production of DIP Containing Newsprint. Wo chenbl. papier 129(14-15): 953-958 August 2001. 11. KURZENDORFER, C.P., LIPHARD, M., RYBINSKI, W., SCHWUGER, M.J. Sodium-Aluminium-Silicates in the Washing Process. Part. IX: Mode of Action of Zeolite A Additive Systems. Colloid & Polymer Sci. 265:542-547 (1987). 12. JAMES, G.V. Water Treatment: A Guide to the Treatment of Water and Effluent Purification. 3rd edition. Technical Press: Edinburgh, 107-127 (1965). 13. BRIGATTI, M.F., FRANCHINI, G., FRIGIERI, P., GARDINALI, L.M., POPPI, L. Treatment of Industrial Wastewater Using Zeolitite and Sepiolite, Natural Microporous Materials. Can. J. Chem. Eng. 77(1):163168 (1999). 14. KEANE, M.A. The Removal of Copper and Nickel from Aqueous Solution Using Y Zeolite Ion Exchangers. Colloids and Surfaces A: Physicochemical and Engineering Aspects 138: 11-20 (1998). 15. MURAKAMI, K., YAMADA, T., KAGA, K., FUDA, K., MATSUNAGA, T. Cation Exchange Properties of Heat-Treated Australian Brown Coal: Influences of Pre-Exchanged Calcium Ions. Colloids and Surfaces A: Physicochemical and Engineering Aspects 193: 153-159 (2001). 16. CURKOVIC, L., CERJAN-STEFANOVIC, S., FILIPAN, T. Metal Ion Exchange by Natural and Modified Zeolites. Wat. Res. 31(6):1379-1382 (1997). 17. CHABOT, B., LORANGER, E. Potentials of Zeolite Materials in the Production of Value-Added Papers. Preprint, 5th Int. Paper Coating Chemistry Symposium, PAPTAC, Montreal, 37-41, 16-19 June (2003). 18. www.pqcorp.com. 19. BROUILLETTE, F., CHABOT, B., MORNEAU, D., DANEAULT, C. Effect of Physicochemical Conditions on the Properties of Zeolite Microparticles. Preprints, 12th Int. Symposium on Wood and Pulping Chemistry, Madison WI, (May 2003). 20. CURKOVIC, L., CERJAN-STEFANOVIC, S., FILIPAN, T. Metal Ion Exchange by Natural and Modified Zeolites. Wat. Res. 31(6):1379-1382 (1997). Résumé: Nous avons étudié la capacité d’extraction des ions calcium contenus dans une eau blanche de machine à papier par une zéolite synthétique (type 4A). Nous avons évalué l’impact de plusieurs paramètres et conditions d’opérations. Les résultats démontrent que la zéolite 4A est très efficace pour éliminer les ions calcium libres contenus dans l’eau blanche. La conductivité, le temps de réaction, la température, le contenu de fibres et de matières extractibles du bois n’ont pas d’effet néfaste sur l’efficacité de la zéolite. Reference: THIBODEAU, J.-B., CHABOT, B., DANEAULT, C. Calcium ion removal by a synthetic zeolite in the manufacture of mechanical grade papers. Pulp & Paper Canada 106(3): T7174 (March, 2005). Paper presented at the 90th Annual Meeting in Montreal, QC, on Jan 26, 2004. Not to be reproduced without permission of PAPTAC. Manuscript received on December 12, 2003. Revised manuscript approved for publication by the Review Panel on May 28, 2004. Keywords: CALCIUM, IONS, REMOVAL, ZEOLITES, WHITE WATER, MECHANICAL PAPERS. 106:3 (2005) ❘❘❘ 45
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