Biogas Purification: A Comparison of Adsorption Performance in D4 Siloxane Removal Between Commercial Activated Carbons and Waste Wood-Derived Char Using Isotherm Equations
Abstract:Biogas production from organic waste could be an option to reduce landfill and pollutant emissions into air, water, and soil. These fuels contain several trace compounds that are crucial for highly efficient energy generators or gas injection into the grid. The ability of adsorbents to physically remove such adsorbates was investigated using adsorption isotherms at a constant temperature. We experimentally modelled isotherms for siloxane removal. Siloxanes were considered due to their high impact on energy gen… Show more
“…The carbon dioxide capacity was determined by monitoring the response of the fixed-bed column with a simulated biogas blend (35% CO 2 and 65% CH 4 ) and identifying the breakthrough time from the data recorded by the mass spectrometer. The co-adsorption effects, like acid gasses (e.g., hydrogen sulphide) and siloxanes [42,43] The biogas flow rate and the GHSV were not changed during the experimental activity; for this reason, their influence on the adsorption capacity was not examined in the current work. The carbon dioxide adsorption capacity was computed using the following equation: 22.4 l mol is the molar volume of an ideal gas; -m sorb (g) is the mass of the sorbent; -10 6 is the unit conversion from ppmv to molar concentration.…”
Section: Co 2 Adsorption Capacitymentioning
confidence: 97%
“…The carbon dioxide capacity was determined by monitoring the response of the fixed-bed column with a simulated biogas blend (35% CO2 and 65% CH4) and identifying the breakthrough time from the data recorded by the mass spectrometer. The co-adsorption effects, like acid gasses (e.g., hydrogen sulphide) and siloxanes [42,43] have not been kept into account in the current study. Other relevant parameters for the adsorption tests are the following:…”
Anaerobically digested sewage sludges were used as feedstock in the production of activated carbons through physical activation. These char samples were experimentally tested as adsorbents for the removal of CO2 from a simulated biogas mixture. The CO2 concentration level allowed in biomethane was fixed from the European Standards EN 16723-1 and EN 16723-2. The char yield and the subsequent adsorption capacity values were studied, considering the operating parameters of the process. A physical activation process was considered with the following parameters: the temperature, the dwell time, the activating agent, the heating rate, the flow rate, and the method. Among the adsorption tests, the activating temperature and the agent employed affected the CO2 removal. The maximum adsorption capacity was achieved with nitrogen as an activating agent at 600 °C, with 2 h of dwell time (102.5 mg/g).
“…The carbon dioxide capacity was determined by monitoring the response of the fixed-bed column with a simulated biogas blend (35% CO 2 and 65% CH 4 ) and identifying the breakthrough time from the data recorded by the mass spectrometer. The co-adsorption effects, like acid gasses (e.g., hydrogen sulphide) and siloxanes [42,43] The biogas flow rate and the GHSV were not changed during the experimental activity; for this reason, their influence on the adsorption capacity was not examined in the current work. The carbon dioxide adsorption capacity was computed using the following equation: 22.4 l mol is the molar volume of an ideal gas; -m sorb (g) is the mass of the sorbent; -10 6 is the unit conversion from ppmv to molar concentration.…”
Section: Co 2 Adsorption Capacitymentioning
confidence: 97%
“…The carbon dioxide capacity was determined by monitoring the response of the fixed-bed column with a simulated biogas blend (35% CO2 and 65% CH4) and identifying the breakthrough time from the data recorded by the mass spectrometer. The co-adsorption effects, like acid gasses (e.g., hydrogen sulphide) and siloxanes [42,43] have not been kept into account in the current study. Other relevant parameters for the adsorption tests are the following:…”
Anaerobically digested sewage sludges were used as feedstock in the production of activated carbons through physical activation. These char samples were experimentally tested as adsorbents for the removal of CO2 from a simulated biogas mixture. The CO2 concentration level allowed in biomethane was fixed from the European Standards EN 16723-1 and EN 16723-2. The char yield and the subsequent adsorption capacity values were studied, considering the operating parameters of the process. A physical activation process was considered with the following parameters: the temperature, the dwell time, the activating agent, the heating rate, the flow rate, and the method. Among the adsorption tests, the activating temperature and the agent employed affected the CO2 removal. The maximum adsorption capacity was achieved with nitrogen as an activating agent at 600 °C, with 2 h of dwell time (102.5 mg/g).
“…Porosity and surface chemistry, coupled to operating conditions (relative humidity, H 2 S concentration, O 2 concentration, presence of other contaminants in biogas stream, and temperature) are the main characteristics that involve the gas cleaning mechanisms [14][15][16][17][18][19][20][21][22].…”
Biochar obtained from sewage sludges are adopted for biogas cleaning. Sewage sludges are treated considering temperature, dwell time, activating agent, heating, and flow rate. The best performances achieved are registered considering the char produced at 400 °C using CO2 as an activating agent with a dwell time of 2 h. The adsorption capacity for the biogas cleaning CH4/CO2/H2S (20 ppm(v)) increased from 1.3 mg/g to 5.9 mg/g with the bed height. Future research with chemical activation processes will be made to improve the adsorption capacity achieved to produce cheaper sorbents than commercial ones.
“…Some of their main characteristics for use as adsorbents are: selectivity on the element (molecule) that it is desired to adsorb or retain on its surface, great adsorption capacity (many pores), and the ability to withstand high temperatures for regeneration. There are many works found on the used of zeolites to adsorb water molecules [1][2][3][4][5][6][7][8][9][10][11]. In particular, García-Soto et al [12] presented an experimental study of a Na-A synthetic zeolite used for separation of the H 2 O/C 2 H 5 OH mixture, at temperatures of 120 and 140 • C , and at each of them different compositions by weight of ethanol: 50%, 60%, 70%, 80%, 85%, 90%, 95%, 97%, and 99%.…”
Adsorption processes are characterized by their kinetics and equilibrium isotherms described by mathematical models. Nowadays, adsorption with molecular sieves is a method used to separate certain elements or molecules from a mixture and produce hydrogen, nitrogen, oxygen, ethanol, or water treatment. This study had two main objectives. The first one was focused on the use of different natural (Clinoptilolite-S.L. Potosi, Clinoptilolite-Puebla, and Heulandite-Sonora) and synthetic (Zeolite Type 3A) adsorbents to separate the mixtures H 2 O/H 2 SO 4 and H 2 O/C 2 H 5 OH. It was determined that both Zeolite Type-3A and Heulandite-Sonora have greater adsorption capacity in a shorter time compared with the Clinoptilolites at different temperatures. The second objective was the simulation of a pressure swing adsorption process to dehydrate ethanol using the parameters obtained from Zeolite Type 3A (with maximum adsorption capacity). Several configurations were considered to calculate the appropriate nominal values for the optimal process. The results illustrate that the purity of ethanol is increased when the following parameters are considered in the adsorption process: a high pressure, a constant temperature between 100 and 120 • C, a feed composition near the azeotropic point with lower water content, and a purge pressure near the vacuum. Finally, the results show that it is possible to take advantage of the length of the absorber bed in order to reduce the energy costs by increasing the ethanol production as well as complying with the international purity standards.
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