Materials Transactions, Vol. 43, No. 5 (2002) pp. 1074 to 1077 Special Issue on Smart Materials-Fundamentals and Applications c 2002 The Japan Institute of Metals Pervaporation Membrane System for the Removal of Ammonia from Water Yasuhiko Hirabayashi Forestry and Forest Products Research Institute, P. O. Box 16, Tsukuba Norin Kenkyu Danchi-nai, Ibaraki 305-8687, Japan Regenerated cellulose and chitosan membranes were studied for the pervaporation separation of an aqueous solution of urine component (ammonia, uric acid or creatinine). The permeation rate of water increased with increase of the temperature of feed solution induced into the upstream side of membrane module. Uric acid, creatine and creatinine were not found in the permeate through the all membranes investigated. Selective permeation of water and ammonia depends on membrane. The removal of ammonia through the chitosan membrane was from 57% to 59%. Adsorption of ammonia from the downstream vapor by silica gels was carried out. And desorption of ammonia from the adsorbents by heating under the reduced pressure to regenerate the capacity of adsorption was also confirmed. In the case of new pervaporation system, the combination of pervaporation and adsorption/desorption process, ammonia was almost completely removed, and finally the pure condensed water was obtained in the cold trap. (Received December 28, 2001; Accepted February 27, 2002) Keywords: pervaporation, ammonia, water, urine, chitosan, membrane 1. Introduction The environmental control and life support system (ECLSS) in the space station is composed of food, air, water, and waste management. The water is important to support human activities in space. The amount of water supply is entirely limited in the space station. Thus the recovery of pure water from urine will be a required subject. Ammonia is a main component of urine. Because of the chemical and physical similarity between water and ammonia, the separation of them is difficult to achieve by microfiltration, ultrafiltration, dialysis, and reverse osmosis. A deterioration of the performance due to the change of surface property of the distillation membrane from hydrophobic to hydrophilic might cause the trouble of direct pass of the urine components to the downstream side. The author has investigated about the pervaporation membrane method for desalination, and demonstrated that the hydrophilic dense membranes, such as cellulose or chitosan membranes, showed the good performance for removing salts from water in one-step operation.1, 2) Therefore it was expected that the pervaporation membrane method would also be good for establishing the water recycle system of ECLSS. The author has demonstrated that the pervaporation through cellulose membranes completely removes nonvolatile compounds from aqueous solution of urine components, such as uric acid, creatine and creatinine, but except for ammonia.3–7) The mechanism of separation by pervaporation is considered to be solubility-diffusion. Pervaporation process generally includes three major steps: preferential sorption of a solute or solvent into the membrane on the feed side, their phase transition from liquid to vapor, and the diffusion of liquid and vapor through the membrane. This means the possibility of separation of aqueous ammonia by pervaporation based on the difference of affinity of water and ammonia to the membrane. However, the separability of aqueous ammonia by pervaporation membrane will be limited to some degree. Therefore, the author designed a new water purification system based on the combination of pervaporation and adsorption/desorption process, as shown in Fig. 1. The down- stream of the pervaporation membrane is a gas phase under reduced pressure; the vapor mixture goes through the adsorption column before reaching to the cold trap. The adsorbent, which selectively adsorbs ammonia from the vapor mixture of water and ammonia, is required. Exposing the adsorbent to the condition of the high vacuum and heat can regenerate the performance of adsorption. Thus the adsorbent can be repeatedly used. The purpose of this work is to find a good performance membrane with better selectivity for ammonia and water, and show the effectiveness of pervaporation followed adsorption/desorption process for removing ammonia. 2. Experimental Procedure 2.1 Pervaporation apparatus A schematic diagram of the pervaporation apparatus is shown in Fig. 2. The feed was continuously circulated from the feed tank (2) through an upstream compartment of membrane cell (5) by a tube pump (1). Feed was kept at the selected temperature by a thermostated water bath (4). The permeation cell was insulated (7) to minimize the heat loss to the atmosphere. In the downstream side the permeated vapor was withdrawn by a vacuum pump (11). In the conventional pervaporation method, the permeate was directly introduced to a cold trap (9) cooled by liquid nitrogen. In the new pervaporation proposed in this study, single adsorption column (8) or double columns in series (or parallel) were set-up between the permeation cell and the cold trap. Permeate was condensed in a cold trap by liquid nitrogen. After preliminary pervaporation for 30 or 60 min to obtain a constant flux, the permeation flax was calculated from the permeation weight of the component in a defined period time and contact area of membrane with feed. Uric acid, creatine and creatinine in feed and permeate solution were analyzed by HPLC (Shimadzu LC-6A) equipped with an UV-VIS detector (Shimadzu SPD-6AV) and a column (Shimpack CLCODS (6.0 mm × 15 cm) heated to 40◦ C. Elution; 20 mmol/L phosphate buffer (pH3.0) with 1.0 mL/min flow rate. Ammonia in feed and permeate solution were determined by an ion chromatography (TOYOSODA) equipped with a conductive Pervaporation Membrane System for the Removal of Ammonia from Water 1075 Fig. 1 Combination of pervaporation and adsorption/desorption process in ECLSS. Fig. 2 Scheme of pervaporation and adsorption apparatus for experiment. detector (TOYOSODA CD-8000) and a column (Shimpack IC-C3 (4.6 mm × 10 cm) heated to 40◦ C. Elution; 25 mmol/L tartaric acid with 1.0 mL/min flow rate. formed was dipped into 1-N aqueous sodium hydroxide solution, washed with water, dried in air again, peeled off from the acrylic resin plate. 2.2 Membranes The film-shaped membranes investigated were cellophane, regenerated cellulose, and chitosan. The membrane structure was examined by a scanning electron microscope (SEM). The regenerated cellulose membrane was obtained by coagulating the cellulose solution of N -methylmorpholine-N -oxide into water, washing and dry. The detail method for preparation of the regenerated cellulose is described in the previous report.4) The chitosan membrane was formed by casting the 1% chitosan solution containing a dilute acetic acid onto an acrylic resin plate and dried in air for 24 to 48 h. The membrane 2.3 Preparation of the silica gel column The adsorbent used was spherical particles silica gel white (5–10 mesh) purchased from Junsei Chemicals Co. Ltd. 10 g of the silica gel was packed in an acrylic resin pipe of 12 mm in inside diameter and 14 cm long. As described in 2.1, single adsorption column (8) or double columns in series (or parallel) were set-ups between the permeation cell and the cold trap. The silica gel adsorbed with ammonia was transferred from the column to vacuum flask, and then the desorption of ammonia was carried out under vacuum (below 1.33 Pa) and heating in the range of 180 and 200◦ C until condensed ma- 1076 Y. Hirabayashi Fig. 3 Cross-sectional SEM photograph of chitosan membrane. Table 1 Results of pervaporation of aqueous feed solution of uric acid, creatine, creatinine, and ammonia through cellophane, regenerated cellulose membrane, and chitosan membrane. Concentration of urine component in feed Uric acid, 0.5 g/L Creatine, 30 mg/L Creatinine, 1.0 g/L Ammonia, 0.1% Concentration of urine components in permeate solution Cellophane Regenerated cellulose membrane Chitosan membrane ND < 0.1 ppm ND < 1 ppm ND < 0.1 ppm 0.08–0.1% ND < 0.1 ppm ND < 1 ppm ND < 0.1 ppm 0.08–0.1% ND < 0.1 ppm ND < 1 ppm ND < 0.1 ppm 0.03–0.04% ND: Non detectable terial was no longer observed in a replaced cold trap. The regenerated silica gel was subjected to the adsorption of ammonia to continue the pervaporation operation. 3. Results and Discussion Figure 3 shows the cross-sectional view of chitosan membrane. Some narrow small cracks or a stripe-like structure running parallel to the surface of membrane were observed, but not perpendicular to the surface. Pervaporation results of the membranes investigated are summarized in Table 1 including the previous results.1–4) Uric acid, creatine and creatinine were not found in the all permeated solution. In accordance with the results of desalination by pervaporation process in which the dense hydrophilic membrane was used, these non-volatile urine compounds did not permeate through the cellulose or chitosan membranes. Table 1 shows that pervaporation process using hydrophilic cellulose membrane, the permeability of ammonia and water is almost equal. This result may indicate that the partition between ammonia and water in the cellulose membrane equals to that in the feed solution. The affinity between cellulose membrane and ammonia is considered to be close to that between cellulose and water. The previous report showed that ammonia preferentially permeates through the hydrophobic membrane. The vapor pressure of ammonia is 1.166 × 106 Pa Fig. 4 Dependence of permeation rate through chitosan membrane on the temperature of feed. and that of water is 4.243 × 103 Pa at +30◦ C. The partial vapor pressure of ammonia of aqueous ammonia will be higher than that of water. In the distillation process, the lower is the boiling point or the higher is the partial pressure, the faster the compound distils away. The pervaporation rate depends on the affinity to membrane material and diffusion in membrane. The affinity of ammonia to hydrophobic material will be stronger than that of water. Taking into account the affinity to membrane. On the other hand, chitosan membrane retards the permeation of ammonia as shown in Table 1. More than 50% of ammonia in feed was rejected by chitosan membrane. Structural unit of chitosan is a derivative of glucose anhydride unit in which the hydroxyl group at 2 position is replaced with amino group. Because of the structural characteristics chitosan will be positively charged in aqueous media. Ammonia is also of course positively charged in aqueous solution. Thus ionic repulsive force, which arises between chitosan and ammonia molecule, impedes the penetration of ammonia into chitosan membrane. On the basis of above discussion pervaporation process of aqueous ammonia through chitosan membrane was investigated in detail. Figure 4 shows the dependence of permeation rate through chitosan membrane on the temperature of feed. The permeation rate increases linearly with increasing in temperature. Table 2 shows the effect of column unit number of adsorbents and the way of connection of the column units on the removal of ammonia at different temperature. Removal (%) is defined as, ((concentration of ammonia in initial feed) − (concentration of ammonia in permeate)) − (concentration of ammonia in initial feed) × 100. Removal of ammonia decrease with increasing in temperature of feed solution. The value of removal of ammonia Pervaporation Membrane System for the Removal of Ammonia from Water 1077 Table 2 Results of pervaporation and pervaporation/adsorption of aqueous ammonia feed solution through chitosan membrane. Number and connection type of adsorbent column Temperat ure of feed (◦ C) Concentratio n of ammonia in feed (%) 0 29.7 35.0 41.4 45.9 50.9 0.989 0.1025 0.0995 0.0999 0.0965 0.0405 0.0442 0.0432 0.0423 0.0403 59.05 56.88 56.58 57.66 58.24 1 34.6 39.7 44.6 51.2 57.1 64.1 0.1310 0.1014 0.0086 0.1044 0.1306 0.1254 0.00015 0.00002 0.00007 0.00024 0.00011 0.00048 99.89 99.98 99.19 99.17 99.92 99.62 2 (Series) 43.9 50.2 55.0 60.1 63.8 68.6 0.1473 0.1489 0.1483 0.1506 0.1459 0.1479 0.000067 0.000697 0.000038 0.000036 0.000052 0.000200 99.95 99.53 99.97 99.96 99.96 99.86 43.9 49.0 57.1 60.6 65.7 71.4 0.1379 0.1403 0.13227 0.1332 0.1311 0.1279 0.000021 0.000038 0.0000097 0.000068 0.000043 0.00022 99.99 99.97 99.99 99.95 99.97 99.83 2 (Parallel) Concentration of ammonia in permeate (%) Removal of ammonia (%) ranged from 78.2% at 41.2 to 39.9% at 56.5◦ C. On the viewpoint of both safety and selectivity, pervaporation operation at mild temperature will be preferable. In any case complete removal of ammonia is difficult by only one step operation of pervaporation. Therefore the author thought out the combination of pervaporation and adsorption process as indicated in Figs. 1 and 2. Silica gel was used as an adsorbent for ammonia, because silica gel can withstand high temperature and high vacuum, and it would release the adsorbed compounds under these conditions to recover the adsorptive activity. Figure 5 indicates that the way of connection of column units affects the dependence of the desorption of ammonia from the adsorbents by heating under the reduced pressure to regenerate the capacity of adsorption was also confirmed. In the case of new pervaporation system, the combination of pervaporation and adsorption/desorption process, ammonia was almost completely removed, and finally the pure condensed water was obtained in the cold trap. It has been cleared that non-volatile main urine Fig. 5 Effect of the way of connection of adsorption column units on the relationship between the permeation rate and temperature of feed. compounds such as uric acid, creatine and creatinine can be completely removed by the pervaporation membrane method using the dense hydrophilic membrane. Therefore, the pervaporation membrane method is promising the very useful system to extract pure water from urine. Acknowledgements This study is carried out as a part of “Ground Research Announcement for Space Utilization” promoted by Japan Space Forum. The authors thank Miss Toshiko Kosa for her excellent technical assistance. REFERENCES 1) Y. Hirabayashi: Chitin and Chitosan Research 1[2] (1995) 92–93. 2) Y. Hirabayashi and G. Kamiyama: Membrane Symposium, [9], (1997) 45–48. 3) Y. Hirabayashi and N. Onishi: Membrane Symposium, [10], (1998) 41– 44. 4) Y. Hirabayashi and N. Onishi: MRS-J Symposium, [10], (1998) 56. 5) Y. Hirabayashi and N. Onishi: The 10th Tsukuba Chemical Engineering Symposium, (1999) 11–12. 6) Y. Hirabayashi and N. Onishi: The 10th Tsukuba Chemical Engineering Symposium, (1999) 13–14. 7) Y. Hirabayashi and N. Onishi: Membrane Symposium, [11], (1999) 89– 92.
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