{'fraction_non_alphanumeric': 0.02651714269026342, 'fraction_numerical': 0.019040943870101044, 'mean_word_length': 4.57538261152719, 'pattern_counts': {'":': 0, '<': 0, '<?xml version=': 0, '>': 0, 'https://': 0, 'lorem ipsum': 0, 'www.': 0, 'xml': 0}, 'pii_count': 0, 'substrings_counts': 0, 'word_list_counts': {'cursed_substrings.json': 7, 'profanity_word_list.json': 0, 'sexual_word_list.json': 0, 'zh_pornsignals.json': 0}}
Hydrogen Recovery from Hydrogen-Methane Gas Mixture Using Coffee Grounds Based Activated Carbon Bioadsorbent

Hydrogen recovery from off-gas of hydrocracking unit by adsorption is one of the process that could increase the efficiency processes of refinery unit. The purpose of this research is to make coffee grounds based activated carbon bioadsorbent that will be used in hydrogen recovery proses. The carbon was prepared by chemical activation using ZnCl2 at temperature 600 o C. The surface area of produced activated carbon was measured using BET and Iodine number, while its surface morphology and composition were characterized using SEM-EDX. The adsorption capacity of activated carbon and its selectivity will be tested using hydrogen-methane gas mixture. The test was carried out on pure methane and hydrogen gas at 20 o C and a mixture of CH4/H2 (mole ratio: 4:1) at 10 o C, 20 o C and 30 o C and pressures from 1 to 6 bars. The results of this study show that the activated carbon can be successfully produced having the specific surface area of 728.07 m 2 /g and the iodine number of 2160 mg/g. The result shows that the adsorption of pure CH4 gas at the same pressure was 2.4 times greater than pure H2. The adsorption test indicates that the produced activated carbon might be used for hydrogen/methane separation.


Introduction
Hydrogen is one of the main intermediate products largely utilized in oil and petrochemical industries. Its usage has been constantly growing in modern refineries, chemical, and petrochemical complexes in order to treat heavier oil feedstock [1]. Generally, in refineries or petrochemical complexes, the off-gas streams contain a considerable amount of hydrogen, which are mostly incinerated in refinery flares as a waste gas [2]. Therefore, the utilization of hydrogen from off-gas can increase process efficiency and reduce production costs. The off-gas produced in refinery unit consists of carbon dioxide, hydrogen, methane, and ethane. Adsorption would be the most suitable technology due to its ability to release either CH 4 or CO 2 and requires lower energy compared to other technologies [3].
One of the key factor that determines the adsorption's process is the adsorbent's characteristic, such as purity, structure, and pore distribution of adsorbent that will affect the surface area and volume of adsorbent. Most commonly used adsorbent is activated carbon, silica gel, alumina, resin, and zeolite due to their high adsorption capacity [4]. Among those adsorbents, activated carbon is the most used adsorbent because it is mainly composed of a carbonaceous material with a high surface area and porous structures. Although it is an excellent adsorbent, it is also very expensive for adsorption. The price of commercial activated carbon in the market is normally from about one thousand dollars to three thousand dollars per ton. Thus, there is a growing demand to find activated carbon with relatively efficient, low cost, and easily available raw material. Generally, activated carbon raw materials are an agricultural waste with lignocellulose and carbon content. Coffee ground is one of the potential activated carbon material due to its availability and cheap price. Based on previous study, coffee ground consists of 47.8% -58.9% carbon, 1.9 -2.3% nitrogen, 0.43 -1.6% ash, and 8.6% cellulose [5].
In the last years, the instant coffee industry has experienced a constant growth as instant coffee has become one of the most popular kinds of coffee drunk by millions of people around the world. As a consequence, large amounts of coffee grounds, which are the solid residues obtained during the processing of coffee powder with hot water or steam to prepare instant coffee, have been generated worldwide (in order of 6 million tons per year) [6].
The aim of this study is to get coffee grounds based activated carbon's characterization such as its surface area, pores volume, and morphology and to evaluate coffee grounds based activated carbon ability to adsorb CH 4 from CH 4 /H 2 mixture in isothermal conditions. This study expected to provide a recommendation of the effectiveness of the coffee grounds used as potential adsorbents' raw material that could be widely produced.

Experimental Methods
This study consists of three parts, which are the preparation of the activated carbon, adsorbent characterization, and the adsorption test. Adsorbent characterization was done with BET analysis, SEM-EDX analysis, and Iodine number. The performance of produced activated carbon is tested on the adsorption of pure hydrogen, pure methane, and gas mixture at 20 o C, and it is also tested to a gas mixture of methane and hydrogen in isothermal condition at 10 o C, 20 o C, and 30 o C with the pressures range of 1 -6 bars.

Materials
The robusta coffee residues as raw material were collected from Starbucks Coffee Shop. All gases used in this study were high purity (99.99%). Deionized water was used to prepare ZnCl 2 and HCl solutions as well as for washing purpose.

Preparation of Activated Carbon
Coffee grounds were first washed with deionized water to remove impurities and then dried at 100 o C for 24 hours. The samples were then crushed and sieved to a particle size of 60 mesh. Afterward, the coffee residues are impregnated with the ZnCl 2 solution with 1 M concentration with ratio 1 gram activated carbon: 10 mL ZnCl 2 solution. The mixture was mixed for 1 hour at room temperature using a hot plate magnetic stirrer and then dried at 110 o C.
The dried samples were activated for 1 h at 600 o C in a pyrolysis reactor under a nitrogen flow of 150 mL/min. The chemical impregnation used temperature of 600 o C to obtain optimal surface area [7]. The weight losses due to activation were determined. The activated carbon was thoroughly washed with deionized water and soaked in 0.1 M hydrochloric acid solution for 30 minutes in order to remove the residual zinc from the pores of the carbons. Afterward, the activated carbon was washed again using hot deionized water until the pH of 6 has been reached and dried in the oven at 110 o C. The dried activated carbon was crushed and sieved to a particle size of 60 mesh.

Characterization of Activated Carbon
The purpose of characterization is to determine the specific surface area, pore volume, morphology, and composition of activated carbon from coffee grounds.
The specific surface area was calculated with the BET method using 0.3 gram of activated carbon samples. Iodine characterization was done to determine the pore volume. A pore volume determined by the amount of adsorbed iodine per gram activated carbon (mg iodine/g activated carbon). 0.1 gram sample was stirred and then heated with 10 mL of iodine solution for 1 hour. Afterward, 5 mL of the mixed solution was titrated by Na 2 SO 3 . The volume of Na 2 SO 3 used for titration then was inputted to iodine number calculation. Meanwhile, morphology and composition of activated carbon were determined using the SEM-EDX method. The purpose of SEM-EDX characterization is to determine whether produced activated carbon has enough pores and to get the composition of produced carbon.

Isothermal Adsorption Test
The adsorption process can be done with several measuring methods, of which one of these is volumetric method. Volumetric methods measure adsorption capacity and ability by using pressure change per hour at a constant temperature. This method of measurement is known as isothermal adsorption. The volumetric method is used in the methane installation, due to the similarity of its parameters with a methane adsorption testing device [8]. The isothermal adsorption experiment was performed based on the mass balance principle, which employs precise measurement of pressure, volumes, and temperatures. The tool used for the adsorption test assembled as in Fig 1. These tools consist of a dozing cylinder, a sampling cylinder, and pressure transducers. The sampling cylinder was fully filled with some amounts of sample. The mass of the sample within the sampling cylinder is determined. The volume void, , in the sampling cylinder was determined by injecting some amounts of inert gas (Helium) into sampling cylinder through dozing cylinder by opening valve 2 while valve 1 and 3 stay closed until the volume of helium in sampling cylinder reached a certain pressure. [9] This experiment used Helium as inert gas because helium is not significantly adsorbed. Therefore, the volume void can be determined by measuring temperatures, pressures, and the amount of injected helium into the sampling cylinder. Helium is injected several times with different pressure to determine the data consistency based on the following.

Fig. 1. Schematic Diagram of the Adsorption Test Apparatus
While the amount of helium injected into the sampling cylinder, � � , was determined by the equation below where V DC represents the volume of dozing cylinder, P i and P f are the initial and final pressure of the dozing cylinder respectively, while R is gas constant and � �� is the compressibility factor of helium gas injected at different pressures. The adsorption test was done with the similar method with three different gasses, which are pure hydrogen, pure methane, and CH 4 /H 2 mixture. The CH 4 /H 2 mixture was made with ratio 2:8. To determine the amount of adsorbed gas in the sampling cylinder, � � , was calculated with Equation 2. The remaining gas presence in the sampling cylinder, � � ���� , in the equilibrium bulk phase is calculated with Equation 3 where � is the pressure when the equilibrium reached in the sampling cylinder and � ���� from Equation 1. The equilibrium reached 30 minutes after the injection process. The amount of adsorbed gas, � ��� , was calculated with Equation 4 .
For multicomponent adsorption, the equation is modified using mol fraction of gas injected and mol fraction of unadsorbed gas as follows.
Where � �,��� is the initial composition of gas mixture while � �,� ���� were determined using GC-TCD analysis. Those steps were repeated with pressure 1 -6 bars sequentially for each gas.
Afterward, %AAD (absolute average deviation) is determined with Gibbs mol adsorption (� ����� ) and the amount of Gibbs mol adsorption from experiment (� ��� ). The %AAD were calculated to determine the error in the experiment with Equation 7.

Result and Discussion
In this section, the characterization of activated carbon obtained and its performance of gas adsorption will be discussed further. Moreover, the Langmuir adsorption model calculation will also be discussed further to determine whether the gas adsorption result fits the Langmuir isothermal model

Adsorbent Preparation and Characterization
The yield of activated carbon obtained was calculated to determine the mass loss of activated carbon during the activation process. The yield of activated carbon obtained shown in Table 1. Based on Table 1, the average yield of activated carbon obtained is 38.03%. A similar study by Alnassar with higher temperature and higher concentration of ZnCl 2 as activating agent showed lower yields of the product [10]. The higher yield of product achieved in this study indicates higher amount of inorganics oxides in the activated carbon obtained during the activation process [10]. At lower concentration, ZnCl 2 reacts with H and O on the surface of activated carbon and forms H 2 O and H 2 , rather than burning away the carbon (CO and CO 2 ), which leads to higher yields [11]. In addition, higher temperature also accelerates dehydration reaction to happen. Therefore, dehydration reaction will evaporate water contain and ZnCl 2 in sample surface area.
The result of the specific surface area using the BET method is 728.07 m 2 /g. A previous study by Haris with similar raw material and activating agent but lower activation temperature shows a lower specific surface area [12]. Higher activation temperature in this study accelerates the volatilization and decomposition of the sample, which leads to an increase in the specific surface area and enhanced pore development [13]. Meanwhile, the result of iodine number is 2160 mg/g. The result shows that produced activated carbon meets the characteristics of commercial activated carbon because it has iodine number greater than 200 mg/g, based on Indonesian National Standard.
The SEM-EDX characterization shows the magnification of produced activated carbon pores and its composition. Based on the result, the produced activated carbon consists of 99.64% carbon, 0.23% oxygen, 0.08% sulphur, 0.03% chloride, 0.02% zinc. The morphology using SEM with magnifications of 1000 times and 1500 times shown in Fig 2 and Fig 3   Fig. 2. SEM-EDX 1000x Magnified

Fig. 3. SEM-EDX 1500x Magnified
According to the SEM images, the produced activated carbon has a highly porous structure which appeared to have a rough texture with heterogeneous surface structure. The white spares on the surface prove the existence of zinc salt residues.
The result of coffee grounds activated carbon's characterization is compared to commercial carbon and the result can be seen in Table 2. Therefore, we can conclude that activated carbon that has been produced in this research can be considered as commercial activated carbon.

Adsorption Test and Modelling
Volume void of activated carbon that has been determined with 4.7 gram activated carbon in the sampling cylinder is 3.26 mL. The void volume of the activated carbon in the sampling cylinder calculated is 3 ml. It is the average of six trials that have been carried out at 1 -6 bars.   Table 3 show the performance comparison between produced coffee grounds based activated carbon and palm shell based activated carbon obtained from the previous research carried out by Putri and Sudibandriyo [9]. It is shown that the adsorption of gas mixture performed with coffee ground based activated carbon is higher than palm oil based activated carbon. It is because a higher surface area allows activated carbon to bind more gas molecules.   Table 4 shows the result of adsorption of pure methane, pure hydrogen, and CH 4 /H 2 mixture in isotherm condition at 20 o C. The optimal adsorption for pure CH 4 gas reaches 0.425 mmol/g, while for the CH 4 /H 2 mixture is 0.249 mmol/g and for pure H 2 reaches 0.181 mmol/g. This result shows that the adsorption of pure CH 4 is higher than CH 4 /H 2 mixture and pure H 2 . This means that the adsorption of pure CH 4 gas at the same pressure is 1.71 times greater than CH 4 (21.5%)/H 2 mixture. Meanwhile, the adsorption of pure CH 4 gas at the same pressure is 2.4 times greater than pure H 2 . Evaluation of composition in unadsorbed CH 4 gas also shows that activated carbon adsorbs most of CH 4 injected. These facts indicate that produced activated carbon might be used for hydrogen/methane separation. Pure CH 4 gas is the most adsorbed than any other gas because of its molecular size. The molecular size of CH 4 and H 2 is 3.8 Å and 2.8 Å respectively, while the mean pore size of activated carbon diameter is 16 Å. This cause the hydrogen molecules do not stay on the surface of the adsorbent but tend to stay in the bulk phase [14].   Table 5 shows the result of CH 4 (21.5%)/H 2 adsorption of coffee based activated carbon at isothermal conditions of 10 and 30 o C. Based on the table, the optimal adsorption was obtained at an isothermal condition at 10 o C with the pressure of 6 bars. The amount of adsorbed gas is 0.321 mmol/g. This amount is 1.3 times higher than the adsorption at 30 o C at the same pressure. This result fits the Le Chatelier principle that states the exothermic reaction would favor lower temperature.
The results of isotherm adsorption obtained from this study presented with a Langmuir isotherm model that described physical interactions between adsorbate and adsorbent molecules as shown in Fig. 5 and Fig. 6. Based on Table 6 and Table 7, it can be seen that the result of pure gas and gas mixture isotherm adsorption test in this study fits Langmuir isothermal adsorption model. This is also supported by the result of %AAD on the adsorption, which is less than 10%. The value of %AAD increase with the increase in temperature because the gas adsorption on the adsorbent will be lower for higher temperature. Therefore, it can be concluded that the suitable Langmuir Model is applied to pure gas and gas mixture in this study.

Conclusion
This study was obtained coffee grounds based activated carbon with a BET surface area of 728.07 m 2 /g and an iodine number of 2160 mg/g. The isotherm adsorption test shows that methane adsorption capacity was the highest then followed by adsorption of CH 4 /H 2 mixture and pure hydrogen respectively. The adsorption of pure CH 4 gas at the same pressure is 2.4 times greater than pure H 2 . Thus, the coffee grounds based activated carbon obtained in this study can be used as bioadsorbent in hydrogen separation from CH 4 /H 2 mixture. The activated carbon produced in this experiment might also be applied in industrial scale, considering the operation condition in hydrogen recovery unit.