Research Article | | Peer-Reviewed

Preparation of Carbon Molecular Sieves in Reducing Atmosphere for Selective O2/N2 Separation

Published in Innovation (Volume 6, Issue 4)
Received: 16 October 2025     Accepted: 30 October 2025     Published: 11 December 2025
Views:       Downloads:
Abstract

Carbon Molecular Sieve (CMS) is an ultramicroporous carbonaceous adsorbent, which is widely used in the field of gas separation, especially for air nitrogen separation, as distinguished from activated carbon due to the uniformity of micropore distribution. The separation of nitrogen from air by pressure swing adsorption (PSA method) using carbon molecular sieve in a medium and small scale nitrogen production process is superior to the conventional air cold separation method. Carbon molecular sieves can be prepared from nuts, wood, polyethylene, polyimide, etc., but we used apricot seed husks as carbon substrates. We analyzed the effect of various factors on the properties of carbon molecular sieves prepared from a matrix of apricot seed husks with extremely low ash content of the matrix and high micropore volume to adsorb oxygen, and on this basis, we established a rational preparation process to prepare CMS for nitrogen gas separation. The properties of the carbon molecular sieves prepared under the optimum preparation conditions were 7.2mg/g oxygen equilibrium adsorption, 6.3mg/g adsorption for 1min and 32 selectivity, which were very good for nitrogen separation. The prepared carbon molecular sieve is highly selective and can be used as a very efficient adsorbent for nitrogen separation in air as well as a support for a highly efficient molecular sieve catalyst.

Published in Innovation (Volume 6, Issue 4)
DOI 10.11648/j.innov.20250604.15
Page(s) 178-186
Creative Commons

This is an Open Access article, distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution and reproduction in any medium or format, provided the original work is properly cited.

Copyright

Copyright © The Author(s), 2025. Published by Science Publishing Group

Keywords

Carbon Molecular Sieve (CMS), Equilibrium Adsorption Capacity, Separation

1. Introduction
CMS is a non-polar carbonaceous adsorbent with a kind of nanoscale ultra-micropores, consisting of fine carbon crystals and amorphous carbon, and has a highly developed pore structure and special surface properties. Because of this special microporous structure, CMS has a higher selectivity than activated carbon in adsorbing the desired component from a gas mixture . The adsorption of gases can be broadly classified as chemical adsorption and physical adsorption. Chemical adsorption method has been widely used in the industry because of low cost, large adsorption, and high selectivity . Whereas, due to the highly corrosive to equipment, high energy consumption and large efficiency loss, chemical adsorption method still needs further improvement . In contrast, solid adsorption exhibits favorable advantages including the absence of corrosivity, the low volatility and the low energy penalty . Separation techniques based on the adsorption kinetics of gas molecules in porous materials such as CMS are used in many fields of the chemical industry and are more practical than conventional separation techniques such as cryogenic distillation or cryogenic adsorption . When gas molecules of different sizes are adsorbed on adsorbents with molecular-sized micropores, the activation energy required for the diffusion of gas molecules in the pores will be different, and consequently the diffusivity of molecules in the pores.
The use of CMS in gas separation processes is usually carried out in two packed bed adsorption columns, called pressure swing adsorption (PSA) . Besides its use in separation processes, CMSs are widely used as catalysts and catalyst supports . Several research groups have tried to prepare carbon molecular sieves to find efficient and economical techniques for gas separation processes.
Basically, carbon-based porous materials such as CMS can be produced by pyrolysis of various natural carbon materials such as coal, crust and wood or by synthetic polymers such as polyvinylidene, polyimide, and phenol-formaldehyde resins . It is generally known that the adsorption properties of carbon molecular sieves are affected by the nature of the precursor, the pyrolysis method, and the post-treatment conditions. Thus, although many studies have been carried out on the manufacture of CMS, the influence of each step of the production process on the product characteristics has not been systematically analyzed, but only limited to the analysis of individual steps. As a result, we did not identify a reasonable process parameter to produce CMS with an efficient characteristic structure. Therefore, in order to improve the technological properties of CMS, we chose new matrix of apricot seed peel with extremely low ash content (less than 2%) and high microporous volume to adsorb oxygen, and hence, we confirmed the conditions of carbonization heat treatment, forming conditions, and pore control, which are suitable for the preparation of CMS for N2/O2 separation.
The CMS produced in this way is widely used in the chemical and metallurgical industries due to its rich source of raw materials and simple manufacturing.
2. Materials and Methods
2.1. Materials
The main raw material, apricot seed shell, benzene (99.9%), high temperature coal tar and coal pitch, the gases N2 (99.998%) and O2 (99.998%), thermosetting resin (novolac resin-401), the 5Å carbon molecular sieve were obtained from the Ponghwa Chemical Factory.
2.2. Preparation of CMS
The process of preparing a carbon molecular sieve for nitrogen separation from a raw material consists of five major steps, as shown in Figure 1.
Figure 1. Process of CMS Manufacturing.
-Carbonization
Approximately 1kg of apricot seed shell, a carbon-containing raw material, was ground to reach a certain particle diameter and placed in a reducing atmosphere in a crucible. Then, the crucible was sealed and carbonized in a CWF-1200 muffle furnace with a thermostat.
-Fine Grinding
Using a conical ball mill (XMQ-240×90) with 500g of carbonaceous material, the particle size of the sample was determined to be less than 10μm. After a certain time of ball milling, the sample was sampled and the particle size distribution was measured using a LS-POP (VI) laser particle size analyzer, and the milling was terminated when the desired particle size was reached.
-Molding
After milling, the raw material, the binder and the auxiliary binder were mixed in a certain proportion and then mixed. The homogeneously mixed material was molded into a Ф2mm×10mm cylinder in a screw extruder.
-Secondary Carbonization
Secondary carbonization is carried out in order to carbonize the binder in the forming step and to bond the carbon together to give a certain strength. After taking a certain amount of molded product into a reducing atmosphere crucible, it was sealed and also subjected to secondary carbonization in a CWF-1200 muffle furnace.
-Porometer Control
Liquid-phase carbon deposition is performed to achieve a uniform pore diameter distribution. A pre-dried deposition precursor of 250g was placed in a vessel containing a certain proportion of benzene and tar, followed by soaking for 24h and drying. The dried sample was placed in a CWF-1200 muffle furnace for carbonization.
2.3. Characterization Evaluation of CMS
2.3.1. Adsorption Characterization Test
The experiments were carried out using a gravimetric adsorption capacity measurement apparatus as shown in Figure 2. In Figure 2, 1 and 2 are vacuum cokes, and the adsorption column consists of a transparent heat-resistant glass tube. A quartz spring is hung on the lid of the heat-resistant glass tube and a sample basket is hung on the end of the quartz spring.
Figure 2. Gravimetric Adsorption Measuring Device.
In Figure 2, the adsorbent sample is first weighed about 0.5~1 g and put into the adsorption column with heat-resistant glassy material. Next, using Cock 1 and 2, the corresponding adsorbate gas as the gas inlet was fed into the adsorption column system and the system was replaced three times. After closing the cock 1 and opening the cock 2, the temperature inside the adsorption column system was heated and desorbed for 3h with a heater at 300°C under reduced pressure by a vacuum pump and then cooled to room temperature. The sensitivity of the quartz spring in the static adsorption measurement device is 21.1mg/mm, and the linear variation is measured with a KM-6 cassette meter with a measurement accuracy of ±0.01mm to determine the adsorption capacity of the adsorbent. The adsorption characteristics were plotted by closing the cock 2 and opening the cock 1 to provide the adsorbate gas to the adsorption chamber and measuring the adsorption amount over time.
From the adsorption characteristics of nitrogen and oxygen gases on the sample, the equilibrium adsorption (adsorption amount when the equilibrium adsorption state is reached, q0), adsorption rate (adsorption amount for 1min, q1min), and selectivity (α) are calculated to compare the properties. In general, the amount of adsorption from the LDF model varies with time according to the following relationship:
(1)
Here
qi: Instantaneous adsorption amount (mg/g) of component i.
qi0: i-component equilibrium adsorption amount (mg/g).
Ki: Apparent mass transfer coefficient (1/s) of the i component.
t: Adsorption elapsed time (s).
Considering the data of the single-component gas adsorption measurements in Eq. (1) and the gravimetric adsorption rate measurement, the selectivity a for KO2 and KN2 is determined by the following equation:
The adsorbate gas used in the experiments was pure, up to 99.998% oxygen or nitrogen gas.
2.3.2. Abrasion Rate Measuring Test
The wear resistance of the prepared samples was measured using a wear rate measuring device (36mm diameter, 300mm length cylindrical). For the measurement of magic rate, 100g of the molded heat-treated sample was put in the wear rate measuring device and rotated at 54rpm for 45min. Then the sample was taken out and the weight (W) of the crushed material less than 1mm was measured.
Then, we find the wear resistance ratio (X, %) according to Eq. (2).
(2)
2.3.3. PSA-N2 Separation Performance Test
The most widely used carbon molecular sieve industry is air separation by pressure swing adsorption. Therefore, by performing air separation using a small variable pressure adsorption experimental setup, it is possible to observe in detail the performance of CMS and propose the best preparation method. The experimental setup is shown in Figure 3.
Operating conditions of the device are as follows:
Boost time tr=5s, time of isostatic pressure tb=0.4s, purge time tp= 0.2s, adsorption pressure Pa=7atm, adsorption half-cycle ta=58s, adsorption column size Ф26 × 1500 mm, adsorption column volume 0.8, adsorption column CMS packing volume 500g (1 column).
The nitrogen generator experimental setup was:
Step 1 - 1 column: Boost, 2 column: Desorption
Step 2 - 1 column: adsorption, 2 column: blowing
Step 3 - 1 column: desorption, 2 column: booster
Step 4 - 1 column: blowing, 2 column: adsorption
Nitrogen production is carried out continuously in this manner. At the moment of reaching the set adsorption pressure, the nitrogen outlet valve of the adsorption column is opened, from which nitrogen is discharged into the nitrogen tank. Finally, the cycling step is the step up, the adsorption step, the blowing step, and the desorption step, depending on how the time of each step is set, the yield and purity of the product nitrogen will vary. These cycles are carried out alternately by two columns. The cycle step operation is controlled by a microcomputer. Generally, the adsorption time and swelling time are chosen to be equal, and the step-up time and desorption time are set equal. The oxygen concentration at the outlet of the PSA column was measured to determine the N2 separation performance of CMS.
Figure 3. PSA Process Experimental Pilot Diagram.
3. Results and Discussion
3.1. Effect of Carbonization Condition
Carbonization was carried out in two stages. Up to temperatures below 400°C with a relatively high salt-dissolving fraction, the heating rate was fixed at v=2°C/min, and the temperature range above 400°C was varied by varying the heating rate, the holding time and the holding temperature. The adsorption characteristics of carbides are shown in Table 1.
Table 1. Oxygen Adsorption Character according to Heat Treatment Condition.

Retention Temperature/°C

Retention Time/h

Rate of Temperature Rise/°C·min-1

Density of Particles /g·mL -1

Balanced Adsorption Quantity

mL/g

mg/ mL

1

650

1

2

1.11

6.2

6.9

2

750

1

2

1.07

7.3

7.8

3

800

1

2

1.21

8.1

9.8

4

850

1

2

1.24

7.5

9.52

5

900

1

2

1.27

7.2

9.1

6

750

4

2

1.07

7.5

8.17

7

850

4

2

1.26

6.9

8.69

8

850

4

2

1.32

6.2

9.8

9

800

1

2

1.21

8.1

9.8

10

800

1

5

1.10

8.4

9.24

11

800

1

10

1.10

8.8

9.13

As shown in Table 1, when the heat treatment temperature is increased above 800°C, the amount of oxygen equilibrium adsorption decreases due to thermal shrinkage. It can be seen that the residence time at the heat treatment temperature t=800°C is longer than 1h, accompanied by the formation of micropores by pyrolysis and the reduction of micropore volume by thermal shrinkage, which leads to an increase in particle density and a decrease in oxygen balance adsorption. In addition, it can be seen that increasing the temperature-programmed rate from v=2°C/min to 10°C/min increases the gravimetric oxygen adsorption capacity (mg/g), but with the overflow of the pyrolysis fraction per unit time, the micropore enlargement occurs and the volume-based adsorption capacity (mg/mL) decreases with decreasing particle density. Therefore, it can be seen that the optimum carbonization heat treatment condition is t=800°C, v=5°C/min and 1h.
3.2. Effect of Molding Condition
Literature review and preliminary experiments confirmed that the optimum forming conditions were different depending on the ash content of the carbides. Therefore, an experimental investigation of the forming conditions suitable for apricot seed-based carbides was carried out and a reasonable forming method was determined. The forming process of the milled carbides is shown in Figure 4.
Figure 4. Molding process of Milling Carbide.
After grinding the carbides to less than 10μm, the thermosetting resin components were mixed with different contents of 10~30% for molding, heat treatment and wear rate measurements are shown in Table 2.
Table 2. Abrasion Rate Determination Result (1).

Carbide Quantity /g

Heating Temperature/°C

Fabric percentage/%

Abrasion Rate/%

1

1

800

10

60

2

1

800

15

63

3

1

800

20

65

4

1

800

25

69

5

1

800

30

72

As shown in Table 2, it can be seen that the wear resistance of the molded heat-treated materials is very low, and therefore, thermosetting resin alone cannot be used as the main binder. The abrasive wear rate was measured with a wear rate measuring device after the formation heat treatment by mixing the pitch and thermosetting resins into the carbides in an organic solvent. According to the results of previous studies, the pitch content for carbides was 10%. The experimental results are shown in Table 3.
Table 3. Abrasion Rate Determination Result (2).

Carbide+Pitch (10%)/g

Heating temperature/°C

Fabric Percentage/%

Abrasion Rate/%

1

1

800

5

93

2

1

800

10

96

3

1

800

15

98.5

4

1

800

20

99.8

As shown in Table 3, the highest wear resistance was observed when the thermosetting resin was molded and heat treated by 20% mixing. From these results, it was confirmed that the thermosetting resin can be used as an auxiliary binder and the optimum binder dosage is 10% pitch and 20% thermosetting resin.
3.3. Effect of Secondary Heat Treatment
The second heat treatment condition was set at a heating rate v=5°C/min, holding time τ=1h and holding temperature t=800°C. The single-component gas adsorption rate characteristics of the compacts after heat treatment are shown in Table 4 below.
Table 4. One Component Gas Adsorption Velocity Character of Modeling After Heating Treatment.

Adsorbate

Heat Treatment Time/h

0.5

1

2

3

5

10

15

20

25

O2/mg·g-1

7.2

7.75

8.44

8.55

9

9.01

9.02

9.02

9.03

N2/mg·g-1

2.08

3.32

4.43

5.68

6.37

7.34

7.35

7.356

7.36

Adsorption Temperature: 20°C, Adsorption Pressure: 0.1MPa
From the experimental results in Table 4, it can be said that after heat treatment, the granular carbides have enough properties as precursors for PSA-N2. First, the rate at which the adsorption equilibrium of oxygen is reached is very fast. The adsorption rate, which is a technical indicator of CMS for PSA-N2, exceeds 80% of the equilibrium oxygen uptake by q021min=7.75mg/g.
3.4. Effect of CMS According to Porometer Control Condition
The experimental results of N2 and O2 adsorption on the molded heat-treated samples by mixing 20% thermosetting resin are shown in Figure 5.
(Molding Heat Treatment using 20% thermosetting resin as an auxiliary binder).

Download: Download full-size image

Figure 5. N2, O2 Adsorption Characterization of Molded Heat Treatment Product.
Figure 6. Adsorption Characteristics of Porometer-Controlled Samples.
a. Tar 33.3%, Benzene 66.7%, b. Tar 35.7%, Benzene 64.3%, c. Tar 38.5%, Benzene 61.5%, d. Tar 41.6%, Benzene 58.4%, e. Tar 43.5%, Benzene 56.6%, f. Tar 45.4%, Benzene- 54.6%
As shown in Figure 5, it can be seen that the molded heat treatment sample has a pore control due to the absence of oxygen adsorption selectivity to nitrogen with a 1min adsorption of 5.78mg/g of oxygen and a 1min adsorption of nitrogen of 4.93mg/g. Pore control of the molded heat-treatment products prepared under the conditions of No. 4 in Table 3 was carried out by immersing 1g of the molded material in a mixture of different amounts of tar and organic solvent for 24h and then annealing at 400°C. The results of the adsorption rate measurements of oxygen and nitrogen gas for six samples with controlled porosity at different compositions of the pore control are shown in Figure 6.
From Figure 6a to f, it can be seen that the case of d) has the highest 1 min adsorption selectivity of oxygen to nitrogen and the equilibrium adsorption amount of oxygen. Of course, a change in tar composition results in an optimum dosage. Considering the adsorption characteristics of CMS prepared according to the heat treatment conditions, such as heat treatment temperature and residence time of molded heat-treated compacts incorporated using a pore regulator consisting of 41.6% tar and 58.4% organic solvent, are shown in Table 5.
Table 5. Adsorption Character of Manufactured CMS.

Heat Treatment Time/°C

Retention Time/h

Oxygen Balanced Adsorption Quantity/ mg·g-1

Rate of Oxygen Adsorption/mg·g-1

Selectivity

1

400

1

5.7

4.6

12

2

500

1

6.3

5.7

17

3

600

1

7.9

6.8

22

4

700

1

8.9

7.3

18

5

800

1

7.2

6.3

32

6

600

2

8.2

7.1

15

7

650

2

8.9

7.2

20

8

750

2

9.1

7.5

18

Table 5 shows that at 700°C, the equilibrium adsorption amount and adsorption rate are the highest, while at 800°C, the equilibrium adsorption amount and adsorption rate are low, but the selectivity is the highest.
3.5. Results of PSA-N2 Separation Performance of the Manufactured CMS
Figure 7. Change of O2 concentration in product gas with space velocity.
The as-prepared seeded CMS was packed in a laboratory PSA-N2 separator and the separation performance was tested. On the other hand, comparative separation experiments with CMS for comparison under the same conditions were carried out. The experimental results are shown in Figure 7.
As shown in Figure 7, the CMS made from apricot seed peel reached close to the CMS performance used for comparison with the nitrogen concentration of 99.2% at the spatial rate SV=0.5 and 99% at SV=1, approaching the time to reach the product concentration equilibrium. As above, we have determined the operating conditions and CMS performance of a PSA device capable of preparing nitrogen with a concentration of 99% for an adsorption pressure of Pa=7atm and an adsorption half-cycle of ta=58s with a CMS made from apricot seed peel. From the above experimental results, we can see that the adsorption properties and wear resistance of our own CMS are much superior.
4. Conclusions
The process and method of preparation of CMS based apricot seed husk were newly established and the nitrogen purity of the PSA-N2 separator was over 99% at SV=1 using this sorbent. The process of preparing carbon molecular sieves using apricot seed shells has five major steps.
The main operating conditions of the process are as follows:
Carbonization heat treatment conditions: holding temperature t=800°C, heating rate v=5°C/min, holding time τ=1h.
Suitable binder dosage: 10% pitch and 20% thermosetting resin.
Secondary heat treatment conditions: holding temperature t=800°C, heating rate v=5°C/min, holding time τ=1h.
The composition of the pore controller: 41.6% tar and 58.4% organic solvent.
Temperature of final heat treatment of molded heat-treated products: Holding temperature t=800°C, heating rate v=5°C/min and holding time τ=1h.
The carbon molecular sieve thus obtained showed very good performance for nitrogen separation, with oxygen balance of 7.2mg/g, 1min adsorption of 6.3mg/g and selectivity of 32.
Abbreviations

CMS

Carbon Molecular Sieve

PSA

Pressure Swing Adsorption

Conflicts of Interest
The authors declare no conflicts of interest.
References
[1] A. Silvestre-Albero, S. Rico-Frances, F. Rodríguez-Reinoso, A. M. Kern, M. Klumpp, B. J. M. Etzold, J. Silvestre-Albero, High selectivity of TiC-CDC for CO2/N2 separation, Carbon. 59 (2013) 221-228.
[2] AS. Bhown, BC. Freeman Analysis and status of post-combustion carbon dioxide capture technologies, Environ Sci Technol. 45(20) (2011) 8624–8632.
[3] N. Mccann, M. Maeder, M. Attalla, Simulation of enthalpy and capacity of CO2 absorption by aqueous amine systems, Ind Eng Chem Res. 47(6) (2008) 2002–2009.
[4] SS. Kapdi, VK. Vijay, SK. Rajesh, R. Prasad, Biogas scrubbing, compression and storage: perspective and prospectus in Indian context. Renew Energ. 30(8) (2005) 1195–1202.
[5] W. Conway, X. G. Wang, D. Fernandes, R. Burns, G. Lawrance, G. Puxty, M. Maeder, Toward the understanding of chemical absorption processes for post-combustion capture of carbon dioxide: electronic and steric considerations from the kinetics of reactions of CO2 (aq) with sterically hindered amines, Environmental Science & Technology. 47 (2013) 1163-1169.
[6] P. Krawiec, E. Kockrick, L. Borchardt, D. Geiger, A. Corma, S. Kaskel, Ordered mesoporous carbide derived carbons: Novel materials for catalysis and adsorption, J. Phys. Chem. C. 113 (2009) 7755-7761.
[7] A. Y. Lo, C. T. Hung, N. Y. Yu, C. T. Kuo, S. B. Liu, Syntheses of carbon porous materials with varied pore sizes and their performances as catalyst supports during methanol oxidation reaction, Appl Energ. 100 (2012) 66-74.
[8] J. Glasel, J. Y. Diao, Z. B. Feng, M. Hilgart, T. Wolker, D. S. Su, B. J. M. Etzold, Mesoporous and graphitic carbide-derived carbons as selective and stable catalysts for the dehydrogenation reaction, Chem. Mater, 27 (2015) 5719-5725.
[9] E. Antolini, Carbon supports for low-temperature fuel cell catalysts, Appl. Catal. B, 88 (2009) 1-24.
[10] B. Hasse, J. Glasel, A. M. Kern, D. Y. Murzin, B. J. M. Etzold, Preparation of carbide-derived carbon supported platinum catalysts, Catal. Today. 249 (2015) 30-37.
[11] F. Zhang, H. Ma, J. Chen, G. D. Li, Y. Zhang, J. S. Chen, Preparation and gas storage of high surface area microporous carbon derived from biomass source cornstalks, Bioresour. Technol. 99 (2008) 4803-4808.
[12] J. Alcaniz-Monge, J. P. Marco-Lozar, D. Lozano-Castello, Monolithic carbon molecular sieves from activated bituminous coal impregnated with a slurry of coal tar pitch, Fuel Process. Technol. 95 (2012) 67-72.
[13] C. Tangsathitkulchai, S. Junpirom, J. Katesa, Comparison of kinetic models for CO2 Gasification of coconut-shell chars: Carbonization Temperature effects on char reactivity and porous properties of produced activated carbons, Engineering Journal. 17 (2013) 13-27.
[14] N. P. Wickramaratne, M. Jaroniec, Phenolic resin-based carbons with ultra-large mesopores prepared in the presence of poly (ethylene oxide)-poly (butylene oxide)-poly (ethylene oxide) triblock copolymer and trimethyl benzene, Carbon. 51 (2013) 45-51.
[15] K. Nakagawa, S. R. Mukai, K. Tamura, H. Tamon, Mesoporous activated carbons from phenolic resins, Chemical Engineering Research & Design. 85 (2007) 1331-1337.
[16] G. C. Laredo, E. Meneses, J. Castillo, J. O. Marroquin, F. Jimeenez-Cruz, Adsorption equilibrium and kinetics of branched octane isomers on a polyvinylidene chloride-based carbon molecular sieve, Energy Fuels. 22 (2008) 2641-2648.
[17] X. Ning, W. J. Koros, Carbon molecular sieve membranes derived from matrimid (R) polyimide for nitrogen/methane separation, Carbon. 66 (2014) 511-522.
Cite This Article
  • APA Style

    Jang, W., Kim, K., Choe, C., Kim, S. (2025). Preparation of Carbon Molecular Sieves in Reducing Atmosphere for Selective O2/N2 Separation. Innovation, 6(4), 178-186. https://doi.org/10.11648/j.innov.20250604.15

    Copy | Download

    ACS Style

    Jang, W.; Kim, K.; Choe, C.; Kim, S. Preparation of Carbon Molecular Sieves in Reducing Atmosphere for Selective O2/N2 Separation. Innovation. 2025, 6(4), 178-186. doi: 10.11648/j.innov.20250604.15

    Copy | Download

    AMA Style

    Jang W, Kim K, Choe C, Kim S. Preparation of Carbon Molecular Sieves in Reducing Atmosphere for Selective O2/N2 Separation. Innovation. 2025;6(4):178-186. doi: 10.11648/j.innov.20250604.15

    Copy | Download

  • @article{10.11648/j.innov.20250604.15,
      author = {Wi-Gwon Jang and Kwang-Guk Kim and Chol-Ryong Choe and Su-Il Kim},
      title = {Preparation of Carbon Molecular Sieves in Reducing Atmosphere for Selective O2/N2 Separation},
      journal = {Innovation},
      volume = {6},
      number = {4},
      pages = {178-186},
      doi = {10.11648/j.innov.20250604.15},
      url = {https://doi.org/10.11648/j.innov.20250604.15},
      eprint = {https://article.sciencepublishinggroup.com/pdf/10.11648.j.innov.20250604.15},
      abstract = {Carbon Molecular Sieve (CMS) is an ultramicroporous carbonaceous adsorbent, which is widely used in the field of gas separation, especially for air nitrogen separation, as distinguished from activated carbon due to the uniformity of micropore distribution. The separation of nitrogen from air by pressure swing adsorption (PSA method) using carbon molecular sieve in a medium and small scale nitrogen production process is superior to the conventional air cold separation method. Carbon molecular sieves can be prepared from nuts, wood, polyethylene, polyimide, etc., but we used apricot seed husks as carbon substrates. We analyzed the effect of various factors on the properties of carbon molecular sieves prepared from a matrix of apricot seed husks with extremely low ash content of the matrix and high micropore volume to adsorb oxygen, and on this basis, we established a rational preparation process to prepare CMS for nitrogen gas separation. The properties of the carbon molecular sieves prepared under the optimum preparation conditions were 7.2mg/g oxygen equilibrium adsorption, 6.3mg/g adsorption for 1min and 32 selectivity, which were very good for nitrogen separation. The prepared carbon molecular sieve is highly selective and can be used as a very efficient adsorbent for nitrogen separation in air as well as a support for a highly efficient molecular sieve catalyst.},
     year = {2025}
    }
    

    Copy | Download

  • TY  - JOUR
    T1  - Preparation of Carbon Molecular Sieves in Reducing Atmosphere for Selective O2/N2 Separation
    AU  - Wi-Gwon Jang
    AU  - Kwang-Guk Kim
    AU  - Chol-Ryong Choe
    AU  - Su-Il Kim
    Y1  - 2025/12/11
    PY  - 2025
    N1  - https://doi.org/10.11648/j.innov.20250604.15
    DO  - 10.11648/j.innov.20250604.15
    T2  - Innovation
    JF  - Innovation
    JO  - Innovation
    SP  - 178
    EP  - 186
    PB  - Science Publishing Group
    SN  - 2994-7138
    UR  - https://doi.org/10.11648/j.innov.20250604.15
    AB  - Carbon Molecular Sieve (CMS) is an ultramicroporous carbonaceous adsorbent, which is widely used in the field of gas separation, especially for air nitrogen separation, as distinguished from activated carbon due to the uniformity of micropore distribution. The separation of nitrogen from air by pressure swing adsorption (PSA method) using carbon molecular sieve in a medium and small scale nitrogen production process is superior to the conventional air cold separation method. Carbon molecular sieves can be prepared from nuts, wood, polyethylene, polyimide, etc., but we used apricot seed husks as carbon substrates. We analyzed the effect of various factors on the properties of carbon molecular sieves prepared from a matrix of apricot seed husks with extremely low ash content of the matrix and high micropore volume to adsorb oxygen, and on this basis, we established a rational preparation process to prepare CMS for nitrogen gas separation. The properties of the carbon molecular sieves prepared under the optimum preparation conditions were 7.2mg/g oxygen equilibrium adsorption, 6.3mg/g adsorption for 1min and 32 selectivity, which were very good for nitrogen separation. The prepared carbon molecular sieve is highly selective and can be used as a very efficient adsorbent for nitrogen separation in air as well as a support for a highly efficient molecular sieve catalyst.
    VL  - 6
    IS  - 4
    ER  - 

    Copy | Download

Author Information
  • Abstract
  • Keywords
  • Document Sections

    1. 1. Introduction
    2. 2. Materials and Methods
    3. 3. Results and Discussion
    4. 4. Conclusions
    Show Full Outline
  • Abbreviations
  • Conflicts of Interest
  • References
  • Cite This Article
  • Author Information