Next Article in Journal
A Mass Consistent Approach to Improve Wind Downscaling for Real Time Fire Spread Simulations
Previous Article in Journal
Combining Wildfire Behaviour Simulations and Connectivity Metrics to Support Wildfire Management
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Proceeding Paper

Effect of Temperature on Sorption and Strength Properties of Regenerated Activated Carbons †

by
Łukasz Winconek
* and
Katarzyna Ignatowicz
Faculty of Civil and Environmental Sciences, Bialystok University of Technology, Wiejska Str. 45E, 15-351 Bialystok, Poland
*
Author to whom correspondence should be addressed.
Presented at Innovations-Sustainability-Modernity-Openness Conference (ISMO’22), Bialystok, Poland, 26–27 May 2022.
Environ. Sci. Proc. 2022, 18(1), 6; https://doi.org/10.3390/environsciproc2022018006
Published: 12 August 2022
(This article belongs to the Proceedings of Innovations-Sustainability-Modernity-Openness Conference (ISMO’22))

Abstract

:
Activated carbon (AC) is produced by either a physical or chemical activation process. It is used in various industries such as water treatment, air purification, and in the processes of clarification, liquid deodorization, and alcohol distillation. They are also used for the recovery of volatile compounds from post-production and waste gases, as well as the recovery of active substances in the pharmaceutical industry. They are also used in technological processes during the production of a number of pharmaceutical, biochemical, and chemical preparations. In order to restore the original physicochemical parameters of granular activated carbon (GAC), we must carry out a regeneration process at high temperature (600–850 °C). During the process, high-pressure steam and carbon dioxide are injected into the regeneration kiln. The conducted research focused on the effect of the temperature of the regeneration process on the sorption and strength parameters of the WG-12 activated carbon samples tested. The entire process was carried out in a laboratory tube kiln MTTF-1200 under identical conditions for both samples. The results showed that the effect of temperature on the regeneration process is very significant. In both cases, it was observed that, as the specified temperature was exceeded, the adsorption capacity and mechanical strength of the tested activated carbon decreased. The efficiency of the process also deteriorated.

Published: 11 August 2022

1. Introduction

Activated carbon (AC) is a porous material with a large specific surface area and increased pore volume. The structure of activated carbon is a disordered system of pores with a diameter from less than one to several hundred nanometers [1,2,3,4,5,6,7,8,9]. AC is characterized by a large specific surface area (1000–3000 m2/g) and a significant pore volume (even above 1 cm3/g) [10,11]. The tested active carbon WG-12 is used in water-treatment processes, both in large water supply stations as well as in small filter and container installations [12,13]. Granular activated carbon (GAC) WG-12, due to its large specific surface area and well-developed pore structure, is highly effective in removing impurities from water. It is also used to dechlorinate water and improve its taste and smell.

2. Material and Methods

We collected two samples of GAC (WG-12) used in the water-treatment process (sample 1 and sample 2). The samples were not fundamentally different because the grain size, raw material, production technology, and physicochemical parameters of the two activated carbons were similar. The activated carbon was dried and analyzed to determine the degree of use. The results are presented in Table 1.
The study consisted of reactivating two activated carbon samples using the same conditions in a laboratory kiln. The test rig consisted of a stationary dryer and a laboratory kiln. The prepared and standardized samples in the amount of 0.2 dm3 were placed in a tube made of steel wire with a mesh 0.5 mm and were reactivated at 600 °C, 650 °C, 700 °C, 750 °C, 800 °C, and 850 °C for 20 min. The experiment was repeated three times to obtain reliable results, and the average values of the three trials were used for the results.

3. Results and Discussion

Table 2 presents obtained results of reactivated carbons.
The results showed that both the activated carbon samples can be regenerated. It was observed that, as the process went on, the sorption capacity and the mechanical strength of the AC decreased. The highest reactivation factor was obtained for temperatures of 700 and 800 degrees, and the lowest for temperatures of 600 and 650 degrees.

4. Conclusions

  • The iodine number increases with increasing temperature (but only up to a certain point).
  • Mechanical strength increases with increasing temperature (but only up to a certain point, then decreases).
  • The efficiency of the regeneration process largely depends on the degree of use of the activated carbon and the content of volatile substances.

Author Contributions

Ł.W. and K.I. conceived and designed the experiments; Ł.W. performed the experiments; Ł.W. and K.I. analyzed the data; Ł.W. contributed materials; Ł.W. wrote the paper. All authors have read and agreed to the published version of the manuscript.

Funding

This work was supported by a research project conducted in the Department of Technology of Environmental Engineering Bialystok University of Technology, No. WZ/WBiNŚ/2/2021.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Yi, H.; Nakabayashi, K.; Yoon, S.-H.; Miyawaki, J. Pressurized physical activation: A simple production method for activated carbon with a highly developed pore structure. Carbon 2021, 183, 735–742. [Google Scholar] [CrossRef]
  2. Bansal, R.C.; Goyal, M. Adsorpcja na w ̨eglu aktywnym. In Adsorption on Activated Carbon; WNT: Warszawa, Poland, 2009. [Google Scholar]
  3. Dębowski, Z. Węgiel Aktywny w Ochronie Środowiska i Przemyśle: Praca Zbiorowa/pod Red. Zygmunta Dębowskiego; Wydawnictwo Politechniki Częstochowskiej: Częstochowa, Poland, 2008. [Google Scholar]
  4. Ignatowicz, K. Occurrence Study of Agrochemical Pollutants in Waters of Suprasl Catchment. Arch. Environ. Prot. 2009, 35, 69–77. [Google Scholar]
  5. Ruthven, D.M. Principles of Adsorption and Adsorptionprocess; John Wiley & Sons Inc.: New York, NY, USA, 2020. [Google Scholar]
  6. Rouquerol, J. Adsorption by Powders and Porous Solids; Academic Press: Cambridge, MA, USA, 2013. [Google Scholar]
  7. Jankowska, H.; Świątkowski, A.; Starostin, L.; Ławinienko-Omiecynska, J. Adsorpcja Jonów na Węglu Aktywnym (Ion Adsorption on Activated Carbon); Wydawnictwo Naukowe PWN: Warsaw, Poland, 1991. [Google Scholar]
  8. Tóth, J. (Ed.) Adsorption: Theory, Modeling, and Analysis; Surfactant Science Series; Marcel Dekker: New York, NY, USA, 2002; ISBN 978-0-8247-0747-7. [Google Scholar]
  9. Ghaedi, M. Adsorption: Fundamental Processes and Applications; Academic Press: Cambridge, MA, USA, 2021. [Google Scholar]
  10. Werle, S.; Dudziak, M.; Sobek, S. Water Solution Purification by Phenol Adsorption on Solid Fraction from Thermal Treatment of Waste Biomass—Occurrences of Unfavourable Phenomenon. Desalin. Water Treat. 2020, 186, 72–77. [Google Scholar] [CrossRef]
  11. Piekarski, J.; Ignatowicz, K.; Dąbrowski, T. Analysis of Selected Methods Use for Calculation of the Coefficients of Adsorption Isotherms and Simplified Equations of Adsorption Dynamics with the Use of IZO Application. Materials 2021, 14, 4192. [Google Scholar] [CrossRef] [PubMed]
  12. Lenort, R.; Stas, D.; Wicher, P.; Holman, D.; Ignatowicz, K. Comparative Study of Sustainable Key Performance Indicators in Metallurgical Industry. Rocz. Ochr. Srodowiska 2017, 19, 36–51. [Google Scholar]
  13. Ignatowicz, K.; Piekarski, J.; Skoczko, I.; Piekutin, J. Analysis of Simplified Equations of Adsorption Dynamics of HCH. Desalination Water Treat. 2016, 57, 1420–1428. [Google Scholar] [CrossRef]
Table 1. The parameters of used activated carbons.
Table 1. The parameters of used activated carbons.
Activated CarbonIodine Number [mg/g]Mechanical Strength [%]Bulk
Density [g/L]
Ash
Content [%]
Volatile
Parts Content [%]
Sample 175795.850112.319.7
Sample 273294.749810.122.3
Table 2. The parameters of reactivated carbons.
Table 2. The parameters of reactivated carbons.
AC [Sample]Process Temperature [°C]Iodine Number [mg/g]Mechanical Strength [%]Bulk
Density [g/L]
Ash
Content [%]
Volatile
Parts Content [%]
160079895.648813.217.2
165082395.248513.615.7
170084994.148015.413.2
175088493.844515.910.5
180087193.842916.810.3
185083492.842217.29.8
260073994.248611.820.1
265074994.146913.216.3
270077893.445214.415.7
275081493.244414.910.9
280082292.942616.210.1
285080191.342417.99.9
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Winconek, Ł.; Ignatowicz, K. Effect of Temperature on Sorption and Strength Properties of Regenerated Activated Carbons. Environ. Sci. Proc. 2022, 18, 6. https://doi.org/10.3390/environsciproc2022018006

AMA Style

Winconek Ł, Ignatowicz K. Effect of Temperature on Sorption and Strength Properties of Regenerated Activated Carbons. Environmental Sciences Proceedings. 2022; 18(1):6. https://doi.org/10.3390/environsciproc2022018006

Chicago/Turabian Style

Winconek, Łukasz, and Katarzyna Ignatowicz. 2022. "Effect of Temperature on Sorption and Strength Properties of Regenerated Activated Carbons" Environmental Sciences Proceedings 18, no. 1: 6. https://doi.org/10.3390/environsciproc2022018006

APA Style

Winconek, Ł., & Ignatowicz, K. (2022). Effect of Temperature on Sorption and Strength Properties of Regenerated Activated Carbons. Environmental Sciences Proceedings, 18(1), 6. https://doi.org/10.3390/environsciproc2022018006

Article Metrics

Back to TopTop