Adsorption of Ammonium Dinitramide (ADN) from Aqueous Solutions

Size: px
Start display at page:

Download "Adsorption of Ammonium Dinitramide (ADN) from Aqueous Solutions"

Transcription

1 Chapter 4 Adsorption of Ammonium Dinitramide (ADN) from Aqueous Solutions Part of the results from this chapter has been published: 1. G. Santhosh, S. Venkatachalam, K.N. Ninan, R. Sadhana. S. Alwan. V. Abarna. M.A. Joseph "Adsorption of ammonium dinitramide (ADN) from aqueous solutions 1. Adsorption on powdered activated charcoal" Journal of Hazardous Materials, 2003, 898, G. Santhosh, S. Venkatachalam, K.N. Ninan, R. Sadhana, "Adsorption of ammonium dinitramide (ADN) from aqueous solutions 2. Adsorption on granular activated charcoal" Adsorption Science and Technology (to be communicated).

2 T HIS CHAPTER details the investigations on the adsorption of ammonium dinitramide (ADN) from aqueous solutions on powdered activated charcoal (PAC) and granular activated charcoal (GAC) in order to find out an effective and cheaper method of separating ADN from aqueous solutions. The effectiveness of PAC and GAC in the selective adsorption of ADN from aqueous solutions of ADN (ADN-F) and ADN in presence of sulphate (sod2-) and nitrate (NO;) ions (ADN-PS) is examined and compared using batch and column methods. The adsorption process follows both Langmuir and Freundlich adsorption isotherms. A detailed study on the use of PAC on the adsorption of ADN is described. The adsorption isotherm parameters for the models are determined. Break-through curves for ADN-F and ADN-PS are obtained for the optimization of separation of ADN from aqueous solutions. Elution curves are generated for the desorption of ADN from PAC using hot water as eluent. The reaction rate constants are determined for the adsorption of ADN over PAC. Langmuir and Freundlich adsorption isotherm parameters for adsorption of ADN over GAC are compared with those of obtained for PAC. The reaction rate constants were determined for the adsorption of ADN on GAC.

3 4.1. Adsorption of ADN on Powdered Activated Charcoal (PAC) & Granular Activated Charcoal (GAC) 4.2 Introduction Much of the work is published on the synthesis of ADN and its analogues [''51. Most of the methods make use of exotic nitrating agents such as N205 or N02BF4 [51. A recent literature reports the synthesis of ADN using conventional nitrating agents such as HN03/H2S04 [61. This process results in ADN along with ammonium sulphate, ((NH4)2S04) and ammonium nitrate (AN, NH4N03) in water. The separation of ADN from aqueous solution involves precipitation, drying, extraction and recrystallization from different solvents and is a time consuming and costly process. The adsorption technique is an effective method of separation at a relatively lower cost in comparison to solvent extraction procedure for many materials. ADN can be adsorbed on a variety of adsorbents like molecular sieves, activated alumina, silica gel, activated charcoal etc., the adsorbed ADN is then eluted with a suitable eluting solvent. Powdered activated charcoal (PAC) & Granular activated charcoal (GAC) were used as adsorbent for the separation of ADN from aqueous solutions. The adsorption behaviour of ADN by PAC & GAC was investigated using Langmulr and Freundlich isotherms. The Langmuir and Freundlich isotherm constants were determined and the amount of PAC & GAC to be used for the adsorption of ADN was also worked out. Breakthrough curves were generated for predicting the column efficiency in the recovery of ADN. Adsorbed ADN was desorbed using hot water as eluent. The reaction rate constants were determined for both the system Experimental Materials Ammonium dinitramide (ADN) was synthesized in our laboratory ['I. It is a pale yellow hygroscopic powder soluble in polar solvents including water. The compound was characterized by UV, IR and thermal methods.

4 The reaction mixture containing ammonium sulphate (3900 mg/l) and ammonium nitrate (3000 mg/l) along with ADN (600 mg/l) was the process solution (ADN-PS), for the adsorption experiments employing PAC. Activated charcoal powder (Sarabhai M. Chemicals Limited, Mumbai, India) with a specific surface area (BET method) of m2g-' and a particle size (Fischer method) of 17km was dried at 110 "C for hrs. and stored in a desiccator prior to use. The process solution (ADN-PS) containing ammonium sulphate (4100 mg~.') and ammonium nitrate (3200 mg~.') along with ammonium dinitramide (500 mg~.') is used for the adsorption experiments using GAC. Granular activated charcoal ( SRL Limited, Mumbai) of particle size 3-5mm was dried at 120 C for 10-12h and stored in a desiccator prior to use Instruments A CARY 5e UV-VIS-NIR spectrometer was used for the measurement of ADN concentration before and after adsorption Adsorption Experiments Adsorption experiments using PAC were conducted by batch and continuous methods at room temperature (30 "C). Batch adsorption experiments were carried out by stirring 3 g of PAC with 100 ml of an aqueous solution of ADN-F or ADN-PS of the desired concentration (0.01 M to 0.1M) in different glass-stoppered erlenmeyer flasks using a magnetic stirrer for predetermined time intervals (30-60 min) till equilibrium was achieved. Column adsorption experiments were carried out on a 20 mm

5 diameter glass column with a sintered disc at the bottom by placing 4 g of PAC and 100 ml solution of ADN-F or ADN-PS of varying concentrations (0.01 M to 0.1 M) at a constant flow rate of 3 mllmin, and the solution after adsorption was collected for different periods of time (30 min intervals). Batch experiments using GAC were conducted at room temperature (30 C). Experiments were carried out by stirring 6g of GAC with 100ml of an aqueous solution of ADN-F or ADN-PS of the desired concentration ( M) in amber coloured stoppered flasks using a magnetic stirrer for predetermined time intervals (30-400min) till equilibrium was achieved. The equilibrium concentration, Ce of the solution was determined by UV spectrophotometer by taking weighed quantities of aliquots of the collected solution. The concentration of ADN adsorbed was obtained by calculating the difference of the concentration of ADN in solution before and after adsorption using the experimentally determined molar extinction co-efficient E ~mo~-"cm-' ['I Results and Discussion Effect of Adsorption Time for PAC & GAC The amount of ADN adsorbed per unit weight of adsorbent (PAC) as a function of time is given in Figure The quantity of ADN adsorbed increas'es with the increase of the adsorption time for ADN-F and ADN-PS. However, it remains constant after an equilibrium time of 175 min for ADN-F and 200 min for ADN-PS, which indicates that the adsorption tends toward saturation at the above-mentioned time.

6 im ADN+ (640 mgl) I. so & Time (mn) Figure 4.1 : The amount of ADN adsorbed per unit weight of PAC as a function of time with 49 of adsorbent at 30 C The amount of ADN adsorbed per unit weight of adsorbent (GAC) as a function of time is given in Figure 4.2. l,. l * l. l. l. l. l.,. l. l. ~ m Time (mn) Figure 4.2: Amount of ADN adsorbed per unit weight of GAC as a function of time with 6g of adsorbent at 30%

7 The quantity of ADN adsorbed increases with the increase of the adsorption time for ADN-F and ADN-PS. It remains constant after an equilibrium time of 350min for ADN-F and 370min for ADN-PS, which indicates that the adsorption tends toward saturation at the abovementioned time. Comparing the equilibrium time taken for the adsorption of ADN on PAC & GAC, the time taken for equilibrium for GAC is almost twice that of PAC, indicating that the equilibrium is achieved fast in the case of adsorption of ADN on PAC Adsorption Isotherms Various isotherm models are available for expressing the adsorption procesi The adsorption isotherm for the adsorbed ADN on PAC & GAC can be analyzed by Langmuir and Freundlich isotherms Langmuir Isotherm The linear representation of the Langmuir isotherm [Io1 can be expressed as in Equation 4.1. where Ce is the equilibrium concentration of ADN in solution (mgll), Ye is the milligrams of adsorbed ADN per gram of adsorbent (mglg), Q is the maximum amount of adsorbed ADN per gram of adsorbent (mglg) and b is the Langmuir constant (Llmg). Thus, a plot of C,/Ye versus Ce should yield a straight line with a slope of 1IQ and an intercept of 11Qb from which the values of Q and b can be readily obtained. Figure. 4.3 shows the plot of Ce/Y, versus C,, which is a straight line with relatively good correlation coefficient (Table 4.1). All the data correctly fit the Langmuir relation and indicating that the adsorption of ADN from aqueous solution on PAC follows the monolayer adsorption.

8 Figure 4.3: Langrnuir plots for the adsorption of ADN on PAC at 30 C The Langrnuir constants obtained from Figure. 4.3 are given in Table 4.1. The Langrnuir equilibrium constant K = Qb was also measured and given in Table 4.1. As it is seen in Table 4.1, the amount of ADN adsorbed per gram of charcoal is higher for ADN-PS compared to ADN-F performed in batch, and the amount of ADN adsorbed is lower for ADN-PS compared to ADN-F performed in column. Since Langmuir theory is restricted to cases where only one layer of molecules can be adsorbed at the surface ["I, the adsorption of ADN from aqueous solutions on PAC follows monolayer adsorption as evident from the observed data fit in Langmuir isotherm.

9 Table 4.1: Langmuir constants from Equation 4.1 at 30 C System Langmuir Constants t Q (mglg) b (Umg) K=Qb (Ug) - ADN-F (Batch) ADN-PS (Batch) ADN-F (Column) I Correlation coefficient (r) ADN-PS (Column) Figure. 4.4 shows the plot of Ce/Ye versus Ce for the batch adsorption of ADN on GAC, which is a straight line with relatively good correlation coefficient (Table 4.2), showing that all the data correctly fit the Langmuir relation and indicating that the adsorption of ADN from aqueous solution on GAC also follows monolayer adsorption. Figure 4.4: Langrnuir plots for the adsorption of ADN on GAC at 30 C Ce

10 The Langmuir constants obtained from Figure 4.4 are given in Table 4.2. The equilibrium constant 'K' was also calculated and given in Table 4.2. The adsorption of ADN from aqueous solutions on GAC follows monolayer adsorption as evident from the observed data fit in Langmuir isotherm. As it is seen from Table 4.2 the amount of ADN adsorbed per gram of GAC is higher for ADN-F than ADN-PS. Table 4.2: Langmuir constants for batch adsorption of ADN on GAC at 30% System ADN-F (Batch) ADN-PS (Batch) Langmuir Constants Q (mglg) b (Umg) K=Qb (L lg) Correlation coefficient (r) Comparison of Table 4.1 & 4.2 reveals that PAC has a better adsorption capacity than GAC. The amount of ADN adsorbed (Q) is much lower on GAC than PAC Freundlich Isotherm The Freundlich adsorption equation [I2] is expressed as given in Equation 4.2. or the linearised form of the equation where P and lln are empirical constants (Freundlich parameters), the values of which are equal to the intercept and slope of the plot of log Ye versus log C,. Freundlich plots for the adsorption of ADN on PAC are shown in Figure. 4.5.

11 The adsorption of ADN on powdered activated charcoal was found to correspond with the Freundlich adsorption isotherm. The Freundlich constants deduced from the straight lines in Figure. 4.5 are given in Table 4.3 along with correlation coefficients. Figure 4.5: Freundlich plots for the adsorption of ADN on PAC at 30 C. Table 4.3: Freundlich constants from Equation 4.3 for adsorption of ADN on PAC at 30 C System ADN-F (Batch) ADN-PS (Batch) ADN-F ( Column) ADN-PS (Column) Freundlich Constants log P n Correlation coefficient (r)

12 For all the experiments, the exponent 'n' is greater than one, which indicates good adsorption of ADN on PAC. The adsorption of ADN from aqueous solutions on PAC follows both Freundlich and Langmuir isotherm as these two fits well with good correlation coefficient (Table 4.1 and 4.3). Freundlich plots for the batch adsorption of ADN on GAC are shown in Figure log C, Figure 4.6: Freundlich plots for the adsorption of ADN on GAC at 30 C The adsorption of ADN on GAC was found to correspond with the Freundlich adsorption isotherm. The Freundlich constants obtained from the straight lines in Figure 4.6 are given in Table 4.4 along with correlation coefficients. For all the experiments, the exponent 'n' is greater than 1, which indicates good adsorption of ADN on GAC. The adsorption of ADN on GAC fits well for both Langmuir and Freundlich isotherms.

13 Table 4.4: Freundlich constants for batch adsorption of ADN on GAC at 30 C - System ADN-F (Batch) ADN-PS (Batch) Freundlich Constants log P n 1.OBI Correlation coefficient (r) Results of Column Adsorption Model for the adsorption of ADN over PAC A reported theoretical model was used in the present study for measuring the change in ADN concentration at the column exit. In a column, the fraction of ADN that is being adsorbed is denoted as 'A' and the fraction of that is remaining in the aqueous solution and passing through the stationary adsorbent is denoted as 'P'. It is assumed that the rate of decrease in the adsorption fraction (A) is proportional to A and P as shown in Equation (4.4 and 4.5). It is noted in Equation 4.5 that P = I-A. Equation 4.5 can be integrated with an initiql condition of A = A, at t = t to get Equation 4.5a. substituting P = I-A, Equation 4.5a becomes Equation 4.5b.

14 defining t, as the adsorption time, as denoted by 2, when P=0.5 (one-half of the adsorption capacity) Equation 4.5b becomes 4.6. The detailed derivation of Equation 4.7 is reported elsewhere [I3]. The derivation of Equation 4.7 is based on the definition that 50% breakthrough of the adsorption process occurs at time 2. Due to the sigmoid nature of the breakthrough curve the adsorbent bed should be completely saturated at 22. ADN fraction (P) passing through the adsorbent column is equal to CICo, where C is the ADN concentration of the exiting aqueous solution at time t and C, is the inlet ADN concentration. Figure 4.7 shows the plots of adsorption time t versus ln[c/(co-c)] for ADN-F and ADN-PS on PAC. It is a straight line with 2 as intercept and Ilk as slope respectively. k and r (model parameters) thus determined are used to construct the breakthrough curve using Equation 4.7. Reasonable linear fit of the data was obtained and the model parameters of the breakthrough curves derived from Figure 4.7 are listed in Table 4.5.

15 Figure 4.7: Linear plots of time, t vs. In[CI(C,-C)] for ADN-F and ADN-PS The breakthrough curves for ADN-F and ADN-PS were constructed using the model parameters s and k listed in Table 4.5 and are given in Figure The calculated breakthrough time for 0.1 mgll of ADN exiting from the column is 75 min for ADN-F and 69 min for ADN-PS. The presence of nitrate and sulphate ions have little effect on the adsorption of ADN on PAC, this is evident from the close breakthrough times observed for ADN-F and ADN-PS. Table 4.5: Model parameters of the breakthrough curves from Figure 4.7. System ADN-F ADN-PS k (Ilmin) s (min) 97 88

16 Figure 4.8: Predicted breakthrough curves for ADN-F and ADN-PS on PAC with a flow rate of 3ml min" and an initial ADN concentration of 6500 mg L-I Desorption of ADN from PAC Desorption studies were performed on ADN-PS adsorbed on PAC using a column at 30 C by placing 49 of PAC and an ADN-PS solution containing 6500 mg/l of ADN. The solution passing through the column was collected and refed 2 to 3 times. The exit solution was analysed by UV and the amount of ADN adsorbed in the column was calculated. The adsorbed ADN was then eluted with hot water (50 C) at a flow rate of 3 ml/min. A plot of the amount of ADN in eluted samples at different time intervals was made and is shown in Figure In a typical run, the amount of ADN adsorbed on PAC for an initial concentration of 6500 mgll is 4300 mg, which is about 66%. The amount of ADN recovered using hot water as eluent is 3850 mg, which is about 89%. These results show higher efficiency of the removal and recovery of ADN on PAC using hot water as

17 eluent. Ion chromatographic analysis of the eluent shows 60 ppm nitrate and 0 ppm sulphate ions. Hence PAC is proved to be efficient in the adsorption of ADN and allows recovery of ADN with hot water. Time (nin) Figure 4.9: Desorption of ADN from PAC with hot water as a function of time with a flow rate of 3.5 ml min-' Determination of Adsorption Rate Constants for PAC and GAC The adsorption rate constants for the adsorption of ADN on PAC & GAC were calculated based on the adsorption rate equation [14*151 given in Equation 4.8. where, adsorption time is 't', adsorption rate constant is 'K', and F=qdq,, 'q; is amount adsorbed at time t, 'q,' is amount adsorbed at equilibrium.

18 A plot of -In(l-F) versus time t gives a straight line for both ADN-F and ADN-PS. The slope of the curve is equal to the adsorption rate constant 'K'. The plot of -In(l-F) versus t for PAC is given in Figure Figure 4.10: Rate constant plots for the adsorption of ADN on PAC The calculated rate constants along with correlation coefficients for ADN-F and ADN-PS for adsorption on PAC are given in Table 4.6. The rate constant for ADN-PS is higher than that of ADN-F showing that the adsorption of ADN from a mixture of sulphate and nitrate ion is better on PAC. Table 4.6: Calculated rate constants for adsorption of ADN on PAC System ADN-F ADN-PS Rate constant (K, min-') 1.49 x 10.~ 2.46 x 10.' Correlation coefficient (r) The adsorption rate constants for the adsorption of ADN on GAC were calculated based on the adsorption rate equation given in 4.8.

19 A plot of -In(l-F) versus time t gives a straight line for both ADN-F and ADN-PS. From the slope of the curve the adsorption rate constant K was calculated. The plot of -In(l-F) versus t is given in Figure Time (mn) Figure : Rate constant plots for the adsorption of ADN on GAC The calculated rate constants along with correlation coefficients for ADN-F and ADN-PS for adsorption on GAC are given in Table 4.7. The rate constant for ADN-PS is slightly higher than that of ADN-F showing that the adsorption of ADN from ADN-PS is better on GAG. Table 4.7: Calculated rate constants for adsorption of ADN on GAC System ADN-F ADN-PS Rate constant (K, min-') 7.72 x IO" 8.05 x Correlation coefficient (r) Comparing the rate constant values obtained for ADN-F & ADN-PS in Table 4.6 & 4.7, the adsorption of ADN is better on PAC than on GAC as evident from the higher rate constant values obtained for the adsorption on PAC.

20 4.5. Conclusions The separation of ADN from aqueous solutions was evaluated in batch and continuous methods, using powdered activated charcoal (PAC) and granular activated charcoal (GAC). The equilibrium concentrations were established for ADN-F and ADN-PS. Langmuir and Freundlich adsorption isotherms were generated for these systems and the equilibrium concentrations were determined. Adsorptive capacities observed were 63.3, 119.0, 105.3, 82.0 mg of ADN per gram of PAC for ADN-F (batch), ADN-PS (batch), ADN-F (column) and ADN-PS (column) respectively. The results revealed that monolayer adsorption isotherms were sufficient to describe the equilibrium adsorption of ADN from aqueous solutions. Theoretical column adsorption model was applied for the prediction of ADN concentration in the exit aqueous solution. The determination of the two model parameters T and k helps in establishing the complete breakthrough curve and is a convenient measure for determining the accurate breakthrough times for separation of ADN from ADN-PS. The calculated rate constant was higher for ADN-PS than for ADN-F. Elution of ADN was achieved by using hot water as eluent. The adsorption of ADN from aqueous solutions was evaluated in batch method using GAC. The equilibrium concentrations were established for ADN-F and ADN-PS. The equilibrium concentrations were determined from Langmuir and Freundlich isotherms for these systems. Adsorptive capacities observed were 35.92, mg of ADN per gram of GAC for ADN-PS and ADN-F respectively. The results on the adsorption of ADN on GAC show that monolayer adsorption isotherms describe the equilibrium adsorption of ADN from aqueous solutions. Adsorption rate constants were determined for ADN-F and ADN-PS; the value is higher for ADN-PS than for ADN-F.

21 4.6. References Schrnitt R.J, Bottaro J.C, Penwell P.E, Bornberger D.C, U.S. Patents , ,1993. Schrnitt R.J, Bottaro J.C, Penwell P.E, Bornberger D.C, U.S. Patent ,1994. Schrnitt R.J, Bottaro J.C, Penwell P.E. Bornberger D.C, U.S. Patent ,1995. Suzuki S, Miazaki S, Hatano H. Shiino K, Onda T, U.S. Patent ,1997. Bottaro J.C, Penwell P.E, Schrnitt R.J, J. Am. Chem. Soc., 1997, 1 19, Langlet Abraham, Ostrnark Henric, Wingborg Niklas. U.S. Patent ,1999. Santhosh G, Venkatachalarn S, Kanakavel M, Ninan K.N, Ind. J. Chem. Technol., 2002, 9, Weber W.J, Mattews A.P, AIChE, 1976, 73, 91.Ruthven D.M. Principles of Adsorption and Adsorption processes, John Wiley, New York, Langrnuir I, J. Am. Chem. Soc., 1918,40,1361. Shoemaker D.P, Garland C.W, Experiments in Physical Chemistry, Mc Graw-Hill, New York, Freundlich H, Colloid and Capillary Chemistry, Matheun, London, Sheng H. Lin, Cheng P. Huang, J. Haz. Mater., 2001, 884, Rarnazan Coskun, Mustafa Yigitoglu, Mehmet Sacak. J.App1. Polym. SCi., 2000, 75, Lu Y, Wu C, Lin W.P, Tang L.Y, Zeng H.M, J. Appl. Polym.Sci., 1994, 22,l.

Chapter 7 Adsorption thermodynamics and recovery of uranium

Chapter 7 Adsorption thermodynamics and recovery of uranium Chapter 7 Adsorption thermodynamics and recovery of uranium 99 Chapter 7. Adsorption thermodynamics and recovery of uranium from aqueous solutions by Spatoglossum 7.1. Materials 7.1.1. Preparation of sorbent

More information

MOF-76: From Luminescent Probe to Highly Efficient U VI Sorption Material

MOF-76: From Luminescent Probe to Highly Efficient U VI Sorption Material MOF-76: From Luminescent Probe to Highly Efficient U VI Sorption Material Weiting Yang, a Zhi-Qiang Bai, b Wei-Qun Shi*, b Li-Yong Yuan, b Tao Tian, a Zhi-Fang Chai*, c Hao Wang, a and Zhong-Ming Sun*

More information

Hydrophobic Silica Aerogels Solvent Removal From Water

Hydrophobic Silica Aerogels Solvent Removal From Water Hydrophobic Silica Aerogels Solvent Removal From Water Zoran NOVAK, Suzana #ERN#I#, Željko KNEZ* University of Maribor, Faculty of Chemistry and Chemical Engineering, Smetanova 17, SI-2000 Maribor, Slovenia

More information

Recap: Introduction 12/1/2015. EVE 402 Air Pollution Generation and Control. Adsorption

Recap: Introduction 12/1/2015. EVE 402 Air Pollution Generation and Control. Adsorption EVE 402 Air Pollution Generation and Control Chapter #6 Lectures Adsorption Recap: Solubility: the extent of absorption into the bulk liquid after the gas has diffused through the interface An internal

More information

Current World Environment Vol. 4(2), (2009)

Current World Environment Vol. 4(2), (2009) Current World Environment Vol. 4(2), 413-417 (2009) Removal of divalent manganese from water by adsorption using gac loaded with Ethylene Di-amine Tetra Acetic acid (EDTA) and Nitrilo Tri-acetic Acid (NTA)

More information

Heavy metal ion uptake properties of polystyrene-supported chelating polymer resins

Heavy metal ion uptake properties of polystyrene-supported chelating polymer resins Proc. Indian Acad. Sci. (Chem. Sci.), Vol. 115, No. 3, June 2003, pp 155 160 Indian Academy of Sciences Heavy metal ion uptake properties of polystyrene-supported chelating polymer resins 1. Introduction

More information

Removal of Copper (II) from Aqueous Solutions using Chalk Powder

Removal of Copper (II) from Aqueous Solutions using Chalk Powder Est. 1984 ORIENTAL JOURNAL OF CHEMISTRY An International Open Free Access, Peer Reviewed Research Journal www.orientjchem.org ISSN: 0970-020 X CODEN: OJCHEG 2013, Vol. 29, No. (2): Pg. 713-717 Removal

More information

AMMONIA ADSORPTION FROM AQUEOUS SOLUTION USING NATURAL ZEOLITES. Faculty of Science, Ubon Ratchathani University, Ubon Ratchathani 31490, Thailand

AMMONIA ADSORPTION FROM AQUEOUS SOLUTION USING NATURAL ZEOLITES. Faculty of Science, Ubon Ratchathani University, Ubon Ratchathani 31490, Thailand AMMONIA ADSORPTION FROM AQUEOUS SOLUTION USING NATURAL ZEOLITES Paradorn Sopa, Pornpan Pungpo * Faculty of Science, Ubon Ratchathani University, Ubon Ratchathani 31490, Thailand * e-mail: pornpan_ubu@yahoo.com

More information

Kinetic and Isotherm Studies of Removal of Metanil Yellow Dye on Mesoporous Aluminophosphate Molecular Sieves

Kinetic and Isotherm Studies of Removal of Metanil Yellow Dye on Mesoporous Aluminophosphate Molecular Sieves Chemical Science Transactions DOI:10.7598/cst2013.15 ISSN/E-ISSN: 2278-3458/2278-3318 RESEARCH ARTICLE Kinetic and Isotherm Studies of Removal of Metanil Yellow Dye on Mesoporous Aluminophosphate Molecular

More information

Removal of Vanadium (V) from water by adsorption using GAC loaded with ethylene di-amine tetra acetic acid (EDTA) and nitrilo tri-acetic acid (NTA)

Removal of Vanadium (V) from water by adsorption using GAC loaded with ethylene di-amine tetra acetic acid (EDTA) and nitrilo tri-acetic acid (NTA) Oriental Journal of Chemistry Vol. 25(3), 799-803 (2009) Removal of Vanadium (V) from water by adsorption using GAC loaded with ethylene di-amine tetra acetic acid (EDTA) and nitrilo tri-acetic acid (NTA)

More information

Adsorption (Ch 12) - mass transfer to an interface

Adsorption (Ch 12) - mass transfer to an interface Adsorption (Ch 12) - mass transfer to an interface (Absorption - mass transfer to another phase) Gas or liquid adsorption (molecular) onto solid surface Porous solids provide high surface area per weight

More information

Studies on the Removal of Rhodamine B and Malachite Green from Aqueous Solutions by Activated Carbon

Studies on the Removal of Rhodamine B and Malachite Green from Aqueous Solutions by Activated Carbon ISSN: 0973-4945; CODEN ECJHAO E- Chemistry http://www.e-journals.net Vol. 5, No.4, pp. 844-852, October 2008 Studies on the Removal of Rhodamine B and Malachite Green from Aqueous Solutions by Activated

More information

ZEOLITES AS ALCOHOL ADSORBENTS FROM AQUEOUS SOLUTIONS

ZEOLITES AS ALCOHOL ADSORBENTS FROM AQUEOUS SOLUTIONS UDC 661.183.6:66.021.3.081.3:547.260.2 APTEFF, 37, 1-192 (2006) BIBLID: 1450 7188 (2006) 37, 83-87 Original scientific paper ZEOLITES AS ALCOHOL ADSORBENTS FROM AQUEOUS SOLUTIONS Blagica Cekova, Dragi

More information

Adsorption of Humic acid on Powdered Activated Carbon (PAC)

Adsorption of Humic acid on Powdered Activated Carbon (PAC) Adsorption of Humic acid on Powdered Activated Carbon (PAC) Department of Civil and Environmental Engineering, MSU, East Lansing, MI, 48824, USA Abstract Removal capacity and rate of Humic Acid (HA) onto

More information

Prelab Reading Assignment: Laboratory Techniques in Organic Chemistry, 4 th Ed. Chapter 19

Prelab Reading Assignment: Laboratory Techniques in Organic Chemistry, 4 th Ed. Chapter 19 CHEM 213 Technique Experiments Experiment 5: Column Chromatography Number of labs - one Reactions performed None Chemicals used: Fluorene-fluorenone mixture, hexanes, methylene chloride, silica gel Supplies

More information

Electronic Supplementary Information

Electronic Supplementary Information Electronic Supplementary Material (ESI) for Journal of Materials Chemistry A. This journal is The Royal Society of Chemistry 2014 Electronic Supplementary Information Micro- and mesoporous poly(schiff-base)s

More information

One-Pot Reaction Cascades Catalyzed by Base and Acid Confined Inside Pores of Mesoporous Silica Nanospheres

One-Pot Reaction Cascades Catalyzed by Base and Acid Confined Inside Pores of Mesoporous Silica Nanospheres One-Pot Reaction Cascades Catalyzed by Base and Acid Confined Inside Pores of Mesoporous Silica Nanospheres Yulin Huang, Brian Trewyn, Hung-ting Chen, Shu Xu, Victor S.-Y. Lin* Department of Chemistry

More information

Application of Fe 2 O 3 nanoparticles in Heavy Metal Removal

Application of Fe 2 O 3 nanoparticles in Heavy Metal Removal Application of Fe 2 O 3 nanoparticles in Heavy Metal Removal 5.1 Introduction Different contaminants are released to water bodies due to the rapid industrialization of human society, including heavy metal

More information

Water and Wastewater Engineering Dr. Ligy Philip Department of Civil Engineering Indian Institute of Technology, Madras. Adsorption Lecture # 34

Water and Wastewater Engineering Dr. Ligy Philip Department of Civil Engineering Indian Institute of Technology, Madras. Adsorption Lecture # 34 Water and Wastewater Engineering Dr. Ligy Philip Department of Civil Engineering Indian Institute of Technology, Madras Adsorption Lecture # 34 Last class we were discussing about advanced wastewater treatment

More information

ADSORPTION STUDIES OF CHROMIUM (VI) ON ACTIVATED CARBON DERIVED FROM CASURINA FRUIT

ADSORPTION STUDIES OF CHROMIUM (VI) ON ACTIVATED CARBON DERIVED FROM CASURINA FRUIT ADSORPTION STUDIES OF CHROMIUM (VI) ON ACTIVATED CARBON DERIVED FROM CASURINA FRUIT Shashikant.R.Mise 1, Ravindra P. Amale 2, Rejendra K.Lamkhade 3 1 Professor, Department of Civil Engineering, PDA College

More information

NOTE. Separation of chlorophenols using columns of hydroxyaluminium interlayered clays

NOTE. Separation of chlorophenols using columns of hydroxyaluminium interlayered clays Clay Minerals (1997) 32, 143-147 NOTE Separation of chlorophenols using columns of hydroxyaluminium interlayered clays Clay minerals play an important role in the retention, transport and chemistry of

More information

SEPARATION OF CITRIC AND LACTIC ACID FROM FERMENTATION LIQUID BY THE CHROMATOGRAPHIC METHOD MODELING AND PARAMETERS ESTIMATION

SEPARATION OF CITRIC AND LACTIC ACID FROM FERMENTATION LIQUID BY THE CHROMATOGRAPHIC METHOD MODELING AND PARAMETERS ESTIMATION SEPARATION OF CITRIC AND LACTIC ACID FROM FERMENTATION LIQUID BY THE CHROMATOGRAPHIC METHOD MODELING AND PARAMETERS ESTIMATION Paweł GLUSZCZ and Jerzy PETERA Faculty of Process and Environmental Engineering,

More information

Adsorption Asmaa Shankar

Adsorption Asmaa Shankar Volume 1, Issue 1, January 2013, Online: Adsorption Asmaa Shankar ABSTRACT This electronic document is a live template. The various components of your paper [title, text, heads, etc.] are already defined

More information

Suggested answers to in-text activities and unit-end exercises. Topic 16 Unit 55

Suggested answers to in-text activities and unit-end exercises. Topic 16 Unit 55 Suggested answers to in-text activities and unit-end exercises In-text activities Discussion (page 117) Some possible ways for minimizing possible sources of error in the experiment: Add a slight excess

More information

Electronic Supplementary Information

Electronic Supplementary Information Electronic Supplementary Information The directing effect of linking unit on building microporous architecture in tetraphenyladmantane-based poly(schiffbase) networks Guiyang Li, Biao Zhang, Jun Yan and

More information

Adsorption of Uranium by Chitin Phosphate and Chitosan Phosphate*

Adsorption of Uranium by Chitin Phosphate and Chitosan Phosphate* Agric. Biol Chem., 45 (10), 2191-2195, 1981 2191 Adsorption of Uranium by Chitin Phosphate and Chitosan Phosphate* Takashi Sakaguchi, Takao Horikoshi and Akira Nakajima Department of Chemistry, Miyazaki

More information

Efficient removal of typical dye and Cr(VI) reduction using N-doped

Efficient removal of typical dye and Cr(VI) reduction using N-doped Electronic Supplementary Material (ESI) for RSC Advances. This journal is The Royal Society of Chemistry 2014 Efficient removal of typical dye and Cr(VI) reduction using N-doped magnetic porous carbon

More information

Removal of Cu 2+, Cd 2+, Hg 2+, and Ag + from Industrial Wastewater by Using Thiol-Loaded Silica Gel

Removal of Cu 2+, Cd 2+, Hg 2+, and Ag + from Industrial Wastewater by Using Thiol-Loaded Silica Gel Universities Research Journal 2011, Vol. 4, No. 3 Removal of Cu 2+, Cd 2+, Hg 2+, and Ag + from Industrial Wastewater by Using Thiol-Loaded Silica Gel Aye Aye Myat 1, Kyaw Naing 2 and San San Myint 1 Abstract

More information

Dry-gel conversion synthesis of Cr-MIL-101 aided by grinding: High surface area high yield synthesis with minimum purification

Dry-gel conversion synthesis of Cr-MIL-101 aided by grinding: High surface area high yield synthesis with minimum purification Electronic Supporting Informations (ESI): Dry-gel conversion synthesis of Cr-MIL-101 aided by grinding: High surface area high yield synthesis with minimum purification Jun Kim, Yu-Ri Lee and Wha-Seung

More information

Removal of Nickel ions from Aqueous Solutions on Packed bed of Zeolite NaX

Removal of Nickel ions from Aqueous Solutions on Packed bed of Zeolite NaX Removal of Nickel ions from Aqueous Solutions on Packed bed of Zeolite NaX Dinesh Kumar a, Sambi S. S. a, Sharma S. K. a, Kumar, V. b a University School of Chemical Technology, GGS IPU, Delhi - 110006,

More information

Lab #3 Reduction of 3-Nitroacetophenone

Lab #3 Reduction of 3-Nitroacetophenone Lab #3 Reduction of 3-Nitroacetophenone Introduction: Extraction: This method uses a different technique in which the two chemical compounds being separated are in immiscible solvents, also known as phases.

More information

Adsorption study on pomegranate peel: Removal of Ni 2+ and Co 2+ from aqueous solution

Adsorption study on pomegranate peel: Removal of Ni 2+ and Co 2+ from aqueous solution ISSN : 0974-746X Adsorption study on pomegranate peel: Removal of Ni 2+ and Co 2+ from aqueous solution Zahra Abbasi 1 *, Mohammad Alikarami 2, Ali Homafar 1 1 Department of Chemistry, Eyvan-e-Gharb Branch,

More information

The Adsorption Isotherms of the Bleaching of Sunflower-Seed Oil

The Adsorption Isotherms of the Bleaching of Sunflower-Seed Oil Tr. J. of Chemistry 22 (1998), 143 148. c TÜBİTAK The Adsorption Isotherms of the Bleaching of Sunflower-Seed Oil Hüseyin TOPALLAR Trakya University, Faculty of Sciences and Letters Department of Chemistry,

More information

Activated Carbon from Sugar Waste Bagasse is used for Removal of Colour from Dye Solution

Activated Carbon from Sugar Waste Bagasse is used for Removal of Colour from Dye Solution International Journal of Research in Advent Technology, Vol.2, No.11, November214 Activated Carbon from Sugar Waste Bagasse is used for Removal of Colour from Dye Solution Amish B. Patel 1 *, Mehul H.

More information

SUPPORTING INFORMATION

SUPPORTING INFORMATION SUPPORTING INFORMATION Copper nanoparticulates in guar-gum: a recyclable catalytic system for the Huisgen[3+2]-Cycloaddition of Azides and Alkynes without additives under ambient conditions Ajeet Kumar,

More information

Laboratory Exercise: Synthesis of Zinc Iodide

Laboratory Exercise: Synthesis of Zinc Iodide CHEM 109 Introduction to Chemistry Revision 1.1 Laboratory Exercise: Synthesis of Zinc Iodide In this exercise we will synthesize the compound Zinc Iodide from the elemental substances Zinc and Iodine.

More information

Tex-620-J, Determining Chloride and Sulfate Contents in Soil

Tex-620-J, Determining Chloride and Sulfate Contents in Soil Contents in Soil Contents: Section 1 Overview...2 Section 2 Sample Preparation...3 Section 3 Ion Chromatography Method...5 Section 4 Wet Chemical Method...9 Section 5 Archived Versions...15 Texas Department

More information

A General Synthesis of Discrete Mesoporous Carbon Microspheres through a Confined Self- Assembly Process in Inverse Opals

A General Synthesis of Discrete Mesoporous Carbon Microspheres through a Confined Self- Assembly Process in Inverse Opals A General Synthesis of Discrete Mesoporous Carbon Microspheres through a Confined Self- Assembly Process in Inverse Opals Zhenkun Sun,, Yong Liu, Bin Li, Jing Wei, Minghong Wang, Qin Yue, Yonghui Deng,

More information

Reactive fluorescent dye functionalized cotton fabric as a Magic Cloth for selective sensing and reversible separation of Cd 2+ in water

Reactive fluorescent dye functionalized cotton fabric as a Magic Cloth for selective sensing and reversible separation of Cd 2+ in water Electronic Supplementary Material (ESI) for Journal of Materials Chemistry C. This journal is The Royal Society of Chemistry 2015 Supplementary Information Reactive fluorescent dye functionalized cotton

More information

Evaluation of adsorptive capacity of natural and burnt kaolinitic clay for removal of congo red dye

Evaluation of adsorptive capacity of natural and burnt kaolinitic clay for removal of congo red dye Available online at www.scholarsresearchlibrary.com Archives of Applied Science Research, 2012, 4 (2):939-946 (http://scholarsresearchlibrary.com/archive.html) ISSN 0975-508X CODEN (USA) AASRC9 Evaluation

More information

Adsorption behavior of methylene blue onto gellan gum-bentonite composite beads for bioremediation application

Adsorption behavior of methylene blue onto gellan gum-bentonite composite beads for bioremediation application World Journal of Pharmaceutical Sciences ISSN (Print): 2321-3310; ISSN (Online): 2321-3086 Published by Atom and Cell Publishers All Rights Reserved Available online at: http://www.wjpsonline.org/ Original

More information

Pressure Swing Adsorption: A Gas Separation & Purification Process

Pressure Swing Adsorption: A Gas Separation & Purification Process Pressure Swing Adsorption: A Gas Separation & Purification Process Pressure swing adsorption is an adsorption-based process that has been used for various gas separation and purification purposes. Separation

More information

Hexavalent Chromium Removal by Quaternized Poly(4-Vinylpyridine) Coated Activated Carbon From Aqueous Solution

Hexavalent Chromium Removal by Quaternized Poly(4-Vinylpyridine) Coated Activated Carbon From Aqueous Solution Hexavalent Chromium Removal by Quaternized Poly(4-Vinylpyridine) Coated Activated Carbon From Aqueous Solution Ravi Kumar Kadari 1, Baolin Deng 2 Dianchen Gang 1 1 West Virginia University Institute of

More information

12 Nicarbazin Nicarbazin (4,4 -dinitro carbanilid (DNC) and 2-hydroxy-4,6-dimethyl pyrimidine (HDP))

12 Nicarbazin Nicarbazin (4,4 -dinitro carbanilid (DNC) and 2-hydroxy-4,6-dimethyl pyrimidine (HDP)) 12 Nicarbazin Nicarbazin (4,4 -dinitro carbanilid (DNC) and 2-hydroxy-4,6-dimethyl pyrimidine (HDP)) O - O - O N + O N + O N NH N H N H O 1,3-bis(4-nitrophenyl)urea, 4,6-dimethyl-1H-pyrimidin-2-one C 13

More information

Cobalt-Porphyrin /Dansyl Piperazine Complex Coated Filter. Paper for Turn on Fluorescence Sensing of Ammonia Gas

Cobalt-Porphyrin /Dansyl Piperazine Complex Coated Filter. Paper for Turn on Fluorescence Sensing of Ammonia Gas Electronic Supplementary Material (ESI) for RSC Advances. This journal is The Royal Society of Chemistry 215 Electronic Supplementary Information Cobalt-Porphyrin /Dansyl Piperazine Complex Coated Filter

More information

Adsorption of Pb(II) Ions on Teak Leaves Activated Carbon- A Kinetic and Equilibrium Study

Adsorption of Pb(II) Ions on Teak Leaves Activated Carbon- A Kinetic and Equilibrium Study Available online at www.pelagiaresearchlibrary.com Pelagia Research Library Der Chemica Sinica, 2010, 1 (2): 35-43 ISSN: 0976-8505 CODEN (USA) CSHIA5 Adsorption of Pb(II) Ions on Teak Leaves Activated

More information

Synthesis, Characterization and Catalytic Activity of MCM-41 Catalyst for Nitration of Phenol

Synthesis, Characterization and Catalytic Activity of MCM-41 Catalyst for Nitration of Phenol http://www.e-journals.in Chemical Science Transactions DOI:10.7598/cst2015.952 2015, 4(2), 438-442 RESEARCH ARTICLE Synthesis, Characterization and Catalytic Activity of MCM-41 Catalyst for Nitration of

More information

Egyptian Petroleum Research Institute BY Rasha Hosny Abdel Mawla Yousef

Egyptian Petroleum Research Institute BY Rasha Hosny Abdel Mawla Yousef Novel Mesoporous Silicas and its Characterizations for Oil Adsorption from Produced Water Injected in Water Injection Projects using Fixed Bed Column Processes BY Rasha Hosny Abdel Mawla Yousef Egyptian

More information

Supporting Information

Supporting Information Electronic Supplementary Material (ESI) for Journal of Materials Chemistry A. This journal is The Royal Society of Chemistry 2017 Supporting Information Cyclic Molecule Aerogels: A Robust Cyclodextrin

More information

Adsorption of Free Fatty Acid from Crude Palm Oil on Magnesium Silicate Derived From Rice Husk

Adsorption of Free Fatty Acid from Crude Palm Oil on Magnesium Silicate Derived From Rice Husk Adsorption of Free Fatty Acid from Crude Palm Oil on Magnesium Silicate Derived From Rice Husk Weerawat Clowutimon, Prakob Kitchaiya, and Pornsawan Assawasaengrat* Department of Chemical Engineering, Faculty

More information

Received: 24 th April-2012 Revised: 07 th May-2012 Accepted: 10 th May-2012 Research article

Received: 24 th April-2012 Revised: 07 th May-2012 Accepted: 10 th May-2012 Research article Received: 24 th April-2012 Revised: 07 th May-2012 Accepted: 10 th May-2012 Research article EQUILIBRIUM ISOTHERM STUDIES OF METHYLENE BLUE FROM AQUEOUS SOLUTION UNTO ACTIVATED CARBON PREPARED FORM STRYCHNOS

More information

Electronic Supplementary Information. Selective Sorption of Light Hydrocarbons on a Family of

Electronic Supplementary Information. Selective Sorption of Light Hydrocarbons on a Family of Electronic Supplementary Information Selective Sorption of Light Hydrocarbons on a Family of Metal-Organic Frameworks with different Imidazolate Pillars Hong-Ru Fu and Jian Zhang* State Key Laboratory

More information

Practical 1 Procedure Iron by Titrimetry

Practical 1 Procedure Iron by Titrimetry Practical 1 Procedure Iron by Titrimetry Introduction This experiment quantifies Fe 2+, ferrous iron, by reacting it with ceric sulphate in a 1:1 reaction, i.e. one mole of ferrous iron reacts with one

More information

Original Research Isotherms for the Sorption of Lead onto Peat: Comparison of Linear and Non-Linear Methods. Yuh-Shan Ho

Original Research Isotherms for the Sorption of Lead onto Peat: Comparison of Linear and Non-Linear Methods. Yuh-Shan Ho Polish Journal of Environmental Studies Vol. 1, No. 1 (26), 81-86 Original Research Isotherms for the Sorption of Lead onto Peat: Comparison of Linear and Non-Linear Methods Department of Environmental

More information

APPLICATION OF ADSORPTION PACKED-BED REACTOR MODEL FOR PHENOL REMOVAL

APPLICATION OF ADSORPTION PACKED-BED REACTOR MODEL FOR PHENOL REMOVAL Tenth International Water Technology Conference, IWTC10 2006, Alexandria, Egypt 131 APPLICATION OF ADSORPTION PACKED-BED REACTOR MODEL FOR PHENOL REMOVAL M. T. Sorour, F. Abdelrasoul and W.A. Ibrahim Sanitary

More information

Pelagia Research Library

Pelagia Research Library Available online at www.pelagiaresearchlibrary.com Der Chemica Sinica, 2014, 5(3):5-9 ISSN: 0976-8505 CODEN (USA) CSHIA5 Removal of Co 2+ ions from aqueous solution by adsorption onto modified granular

More information

Removal of Organic Contents from Wastewater Using Leusas aspera

Removal of Organic Contents from Wastewater Using Leusas aspera Research Journal of Chemical and Environmental Sciences Res J. Chem. Environ. Sci. Vol 2 [6] December 2014: 46-53 Online ISSN 2321-1040 CODEN: RJCEA2 [USA] Academy for Environment and Life Sciences, INDIA

More information

Adsorption Equilibria. Ali Ahmadpour Chemical Eng. Dept. Ferdowsi University of Mashhad

Adsorption Equilibria. Ali Ahmadpour Chemical Eng. Dept. Ferdowsi University of Mashhad Adsorption Equilibria Ali Ahmadpour Chemical Eng. Dept. Ferdowsi University of Mashhad Contents Introduction Adsorption isotherm models Langmuir isotherm Volmer isotherm Fowler-Guggenheim isotherm Hill-deBoer

More information

Chapter No. 2 EXPERIMENTAL TECHNIQUES IN CHEMISTRY SHORT QUESTIONS WITH ANSWERS Q.1 Define analytical chemistry? The branch of chemistry which deals with the qualitative and quantitative analyses of sample

More information

Supplementary Material (ESI) for CrystEngComm. An ideal metal-organic rhombic dodecahedron for highly efficient

Supplementary Material (ESI) for CrystEngComm. An ideal metal-organic rhombic dodecahedron for highly efficient Supplementary Material (ESI) for CrystEngComm An ideal metal-organic rhombic dodecahedron for highly efficient adsorption of dyes in an aqueous solution Yuan-Chun He, Jin Yang,* Wei-Qiu Kan, and Jian-Fang

More information

Supporting Information

Supporting Information Supporting Information An L-proline Functionalized Metallo-organic Triangle as Size-Selective Homogeneous Catalyst for Asymmertry Catalyzing Aldol Reactions Xiao Wu, Cheng He, Xiang Wu, Siyi Qu and Chunying

More information

Batch system example (previous midterm question)

Batch system example (previous midterm question) Batch system example (previous midterm question) You are to design a batch adsorber to remove an organic contaminant (A) from 400L of aqueous solution containing 0.05g/L of the contaminant. To facilitate

More information

Supporting Information. Adsorption of Cu(II), Zn(II), and Pb(II) from aqueous single. and binary metal solutions by regenerated cellulose and

Supporting Information. Adsorption of Cu(II), Zn(II), and Pb(II) from aqueous single. and binary metal solutions by regenerated cellulose and Electronic Supplementary Material (ESI) for RSC Advances. This journal is The Royal Society of Chemistry 2018 Supporting Information Adsorption of Cu(II), Zn(II), and Pb(II) from aqueous single and binary

More information

Qingdao Institute of Bioenergy and Bioprocess Technology, Chinese Academy of Science,

Qingdao Institute of Bioenergy and Bioprocess Technology, Chinese Academy of Science, Supporting information A rht type Metal-Organic Framework based on Small Cubicuboctahedron Supermolecular Building Blocks and Adsorption Properties Liangjun Li a,b, Sifu Tang a, Xiaoxia Lv a,b, Min Jiang

More information

Dye Removal Using Peat

Dye Removal Using Peat Dye Removal Using Peat By Konduru R. Ramakrishna, T. Viraraghavan Faculty of Engineering, University of Regina, Saskatchewan, Canada The textile industry, a major consumer of water for several of its wet

More information

Adsorption of chromium from aqueous solution by activated alumina and activated charcoal

Adsorption of chromium from aqueous solution by activated alumina and activated charcoal Adsorption of chromium from aqueous solution by activated alumina and activated charcoal Suman Mor a,b*, Khaiwal Ravindra c and N. R. Bishnoi b a Department of Energy and Environmental Science, Chaudhary

More information

Please do not adjust margins. Flower stamen-like porous boron carbon nitride nanoscrolls for water cleaning

Please do not adjust margins. Flower stamen-like porous boron carbon nitride nanoscrolls for water cleaning Electronic Supplementary Material (ESI) for Nanoscale. This journal is The Royal Society of Chemistry Please do 2017 not adjust margins Electronic Supplementary Information (ESI) Flower stamen-like porous

More information

Removal Of Copper From Waste Water Using Low Cost Adsorbent

Removal Of Copper From Waste Water Using Low Cost Adsorbent IOSR Journal of Applied Chemistry (IOSR-JAC) e-issn: 2278-5736. Volume 3, Issue 6 (Jan. Feb. 2013), PP 51-55 Removal Of Copper From Waste Water Using Low Cost Adsorbent Jubraj Khamari* Sanjeet Kumar Tiwari**

More information

2017 Reaction of cinnamic acid chloride with ammonia to cinnamic acid amide

2017 Reaction of cinnamic acid chloride with ammonia to cinnamic acid amide 217 Reaction of cinnamic acid chloride with ammonia to cinnamic acid amide O O Cl NH 3 NH 2 C 9 H 7 ClO (166.6) (17.) C 9 H 9 NO (147.2) Classification Reaction types and substance classes reaction of

More information

Copper biosorption in a column of pretreated Aspergillus niger biomass

Copper biosorption in a column of pretreated Aspergillus niger biomass Copper biosorption in a column of pretreated Aspergillus niger biomass Mausumi Mukhopadhyay a, S.B. Noronha a, G.K. Suraishkumar b a Department of Chemical Engineering, Indian Institute of Technology Bombay,

More information

Distinguish quantitatively between the adsorption isotherms of Gibbs, Freundlich and Langmuir.

Distinguish quantitatively between the adsorption isotherms of Gibbs, Freundlich and Langmuir. Module 8 : Surface Chemistry Lecture 36 : Adsorption Objectives After studying this lecture, you will be able to Distinguish between physisorption and chemisorption. Distinguish between monolayer adsorption

More information

Supporting Information

Supporting Information Supporting Information Precision Synthesis of Poly(-hexylpyrrole) and its Diblock Copolymer with Poly(p-phenylene) via Catalyst-Transfer Polycondensation Akihiro Yokoyama, Akira Kato, Ryo Miyakoshi, and

More information

not to be republished NCERT MOST of the reactions are carried out at atmospheric pressure, hence THERMOCHEMICAL MEASUREMENT UNIT-3

not to be republished NCERT MOST of the reactions are carried out at atmospheric pressure, hence THERMOCHEMICAL MEASUREMENT UNIT-3 UNIT-3 THERMOCHEMICAL MEASUREMENT MOST of the reactions are carried out at atmospheric pressure, hence heat changes noted for these reactions are enthalpy changes. Enthalpy changes are directly related

More information

A Facile and High-Recovery Material for Rare Metals Based on a Water- Soluble Polyallylamine with Side-Chain Thiourea Groups

A Facile and High-Recovery Material for Rare Metals Based on a Water- Soluble Polyallylamine with Side-Chain Thiourea Groups Manuscript for Supporting Information A Facile and High-Recovery Material for Rare Metals Based on a Water- Soluble Polyallylamine with Side-Chain Thiourea Groups Daisuke Nagai*, Megumi Yoshida, Takuya

More information

Simultaneous Adsorption and Biodegradation of Phenol and Cyanide in Multicomponent System

Simultaneous Adsorption and Biodegradation of Phenol and Cyanide in Multicomponent System International Journal of Environmental Engineering and Management. ISSN 2231-1319, Volume 4, Number 3 (2013), pp. 233-238 Research India Publications http://www.ripublication.com/ ijeem.htm Simultaneous

More information

Supporting Information

Supporting Information Supporting Information Supramolecular design for polymer/titanium oxo-cluster hybrids: An open door to new organic-inorganic dynamers Fabien Périneau, Sandrine Pensec, Clément Sanchez, Costantino Creton,

More information

A New Model for Asymmetric Amplification in Amino Acid Catalysis - Supporting information

A New Model for Asymmetric Amplification in Amino Acid Catalysis - Supporting information A New Model for Asymmetric Amplification in Amino Acid Catalysis - Supporting information Martin Klussmann, Hiroshi Iwamura, Suju P. Mathew, David H. Wells, Urvish Pandya, Alan Armstrong and Donna G. Blackmond

More information

CHEM 254 EXPERIMENT 5. Solubility and Enthalpy of Fusion of Ammonium Oxalate in Water

CHEM 254 EXPERIMENT 5. Solubility and Enthalpy of Fusion of Ammonium Oxalate in Water CHEM 254 EXPERIMENT 5 Solubility and Enthalpy of Fusion of Ammonium Oxalate in Water In general solubility (g/100 ml) is defined as amount of substance that dissolved in a given solvent at a given temperature.

More information

Uranium biosorption by Spatoglossum asperum J. Agardh:

Uranium biosorption by Spatoglossum asperum J. Agardh: Chapter 6 Uranium biosorption by Spatoglossum asperum J. Agardh: 76 Chapter 6. Uranium biosorption by Spatoglossum asperum J. Agardh: Characterization and equilibrium studies. 6.1. Materials 6.1.1. Collection

More information

Absorption of Phenol and Methylene Blue by Activated Carbon from Pecan Shells 1

Absorption of Phenol and Methylene Blue by Activated Carbon from Pecan Shells 1 ISSN 6-9X, Colloid Journal, 7, Vol. 69, No., pp. 9. Pleiades Publishing, Ltd., 7. Absorption of Phenol and Methylene Blue by Activated Carbon from Pecan Shells R. A. Shawabkeh a and E. S. M. Abu-Nameh

More information

MOST of the reactions are carried out at atmospheric pressure, hence

MOST of the reactions are carried out at atmospheric pressure, hence MOST of the reactions are carried out at atmospheric pressure, hence heat changes noted for these reactions are enthalpy changes. Enthalpy changes are directly related to the temperature changes by the

More information

Research in Chemistry and Environment

Research in Chemistry and Environment International Journal of Research in Chemistry and Environment Available online at: www.ijrce.org ISSN 2248-9649 Research Paper Adsorption of Eosin Dyes Onto Activated Carbon Prepared from Wood of Adina

More information

Electronic Supplementary Information. Noninvasive Functionalization of Polymers of Intrinsic Microporosity for Enhanced CO 2 Capture

Electronic Supplementary Information. Noninvasive Functionalization of Polymers of Intrinsic Microporosity for Enhanced CO 2 Capture Electronic Supplementary Information Noninvasive Functionalization of Polymers of Intrinsic Microporosity for Enhanced CO 2 Capture Hasmukh A. Patel and Cafer T. Yavuz* Oxide and Organic Nanomaterials

More information

Adsorption equilibrium and dynamics of toluene vapors onto three kinds of silica gels

Adsorption equilibrium and dynamics of toluene vapors onto three kinds of silica gels IOP Conference Series: Materials Science and Engineering PAPER OPEN ACCESS Adsorption equilibrium and dynamics of toluene vapors onto three kinds of silica gels To cite this article: K L Yan and Q Wang

More information

Adsorption and Catalysis. Radha V Jayaram Institute of Chemical Technology, Mumbai

Adsorption and Catalysis. Radha V Jayaram Institute of Chemical Technology, Mumbai Adsorption and Catalysis Radha V Jayaram Institute of Chemical Technology, Mumbai 1 2 Different solids would adsorb different amounts of the same gas even under similar conditions. Substances like charcoal

More information

CHAPTER CHROMATOGRAPHIC METHODS OF SEPARATIONS

CHAPTER CHROMATOGRAPHIC METHODS OF SEPARATIONS Islamic University in Madinah Department of Chemistry CHAPTER - ----- CHROMATOGRAPHIC METHODS OF SEPARATIONS Prepared By Dr. Khalid Ahmad Shadid Chemistry Department Islamic University in Madinah TRADITIONAL

More information

Supporting Information

Supporting Information Supporting Information Photocatalytic Suzuki Coupling Reaction using Conjugated Microporous Polymer with Immobilized Palladium Nanoparticles under Visible Light Zi Jun Wang, Saman Ghasimi, Katharina Landfester

More information

Carbon Dots Modified Mesoporous Organosilica as an Adsorbent for the. Removal of 2, 4-Dichlorophenol and Heavy Metal Ions

Carbon Dots Modified Mesoporous Organosilica as an Adsorbent for the. Removal of 2, 4-Dichlorophenol and Heavy Metal Ions Electronic Supplementary Material (ESI) for Journal of Materials Chemistry A. This journal is The Royal Society of Chemistry 2015 Electronic Supplementary Information (ESI) for Journal of Materials Chemistry

More information

ASTM Designation: D Standard Test Method for Determination of Iodine Number of Activated Carbon

ASTM Designation: D Standard Test Method for Determination of Iodine Number of Activated Carbon ASTM Designation: D4607-94 Standard Test Method for Determination of Iodine Number of Activated Carbon 1. Scope 1.1 This test method covers the determination of the relative activation level of unused

More information

Supporting Information

Supporting Information Supporting Information Hydrogen Storage in the Dehydrated Prussian Blue Analogues M 3 [Co(CN) 6 ] 2 (M = Mn, Fe, Co, Ni, Cu, Zn) Steven S. Kaye and Jeffrey R. Long* Dept. of Chemistry, University of California,

More information

TLC Separation of Nitrophenones on Polar Adsorbents

TLC Separation of Nitrophenones on Polar Adsorbents International Journal of hemistry and Applications. ISSN 0974-3111 Volume 5, Number 1 (2013), pp. 61-71 International Research Publication House http://www.irphouse.com TL Separation of Nitrophenones on

More information

Adsorption of Ethylacetate from Ethyl Acetate Water Mixture using Activated Clay

Adsorption of Ethylacetate from Ethyl Acetate Water Mixture using Activated Clay Adsorption of Ethylacetate from Ethyl Acetate Water Mixture using Activated Clay N.V. Ohaa, P.k. Igbokwe, I.A. Obiora-Okafo, E.M. Ejikeme and R.M. Government Department of Chemical Engineering, Faculty

More information

Removal of Fluoride from Synthetic Water Using Chitosan as an Adsorbent

Removal of Fluoride from Synthetic Water Using Chitosan as an Adsorbent IOSR Journal of Environmental Science, Toxicology and Food Technology (IOSR-JESTFT) e-issn: 2319-2402,p- ISSN: 2319-2399.Volume 12, Issue 4 Ver. II (April. 2018), PP 43-48 www.iosrjournals.org Removal

More information

Supporting information A Porous Zr-cluster-based Cationic Metal-Organic Framework for Highly Efficient Cr 2 O 7

Supporting information A Porous Zr-cluster-based Cationic Metal-Organic Framework for Highly Efficient Cr 2 O 7 Electronic Supplementary Material (ESI) for ChemComm. This journal is The Royal Society of Chemistry 2015 Supporting information A Porous Zr-cluster-based Cationic Metal-Organic Framework for Highly Efficient

More information

Supporting Information for: Separation in biorefineries by liquid phase adsorption: itaconic acid as case study

Supporting Information for: Separation in biorefineries by liquid phase adsorption: itaconic acid as case study Supporting Information for: Separation in biorefineries by liquid phase adsorption: itaconic acid as case study Kai Schute, 1 Chaline Detoni, 1,2 Anna, Kann 1, Oliver Jung 1, Regina Palkovits, 1 * and

More information

Chromatography Extraction and purification of Chlorophyll CHM 220

Chromatography Extraction and purification of Chlorophyll CHM 220 INTRODUCTION Extraction and purification of naturally occurring molecules is of the most common methods of obtaining organic molecules. Locating and identifying molecules found in flora and fauna can provide

More information

Adsorption of Methylene Blue on Mesoporous SBA 15 in Ethanol water Solution with Different Proportions

Adsorption of Methylene Blue on Mesoporous SBA 15 in Ethanol water Solution with Different Proportions 2015 2 nd International Conference on Material Engineering and Application (ICMEA 2015) ISBN: 978-1-60595-323-6 Adsorption of Methylene Blue on Mesoporous SBA 15 in Ethanol water Solution with Different

More information

Katarzyna Zielińska, Alexandre G. Chostenko, Stanisław Truszkowski

Katarzyna Zielińska, Alexandre G. Chostenko, Stanisław Truszkowski ADSORPTION OF CADMIUM IONS ON CHITOSAN MEMBRANES: KINETICS AND EQUILIBRIUM STUDIES Katarzyna Zielińska, Alexandre G. Chostenko, Stanisław Truszkowski Chair of Nuclear and Radiation Chemistry Faculty of

More information

Removal of Basic Dyes from Aqueous Solutions by Sugar Can Stalks

Removal of Basic Dyes from Aqueous Solutions by Sugar Can Stalks Available online at www.pelagiaresearchlibrary.com Advances in Applied Science Research, 2011, 2 (4):283-290 ISSN: 0976-8610 CODEN (USA): AASRFC Removal of Basic Dyes from Aqueous Solutions by Sugar Can

More information

SUPPLEMENTARY INFORMATION

SUPPLEMENTARY INFORMATION SUPPLEMENTARY INRMATIN doi:10.1038/nature16185 Improved Synthesis of P-CDP H H H 7 + 1 TH/DM: 9/1 K 2 C 3 / 85 o C 2 days / under N 2 45% H R R 7 P-CDP 2 n A flame dried 20 ml scintillation vial equipped

More information