, Volume 25, Issue 3, pp 327–336 | Cite as

Application of microwave heating in the preparation of functionalized activated carbons

  • Małgorzata GilEmail author
  • Sylwia Pasieczna-Patkowska
  • Piotr Nowicki
Open Access


A series of modified carbonaceous materials has been obtained via nitrogenation, oxidation and thermal treatment of peat-based activated carbons with the use of microwave heating. In order to obtain materials characterised by diverse functional groups content, both in terms of the type and quantity, the starting material was subjected to four different treatment: (1) oxidation with nitric acid followed by heat treatment at 600 °C, (2) oxidation with hydrogen peroxide followed by heat treatment at 600 °C, (3) annealing in nitrogen atmosphere at 900 °C and (4) impregnation with urea followed by heat treatment at 800 °C. All the materials under investigation were characterised by elementary analysis, surface area measurements, estimation of the number of surface functional groups as well as by thermal analysis and photoacoustic and mass spectroscopy. Depending on the procedure of modification, the final products were activated carbons of medium developed surface area ranging from 582 to 657 m2/g, showing basic or intermediate acidic-basic character of the surface and different content of surface functional groups varying from 0.57 to 1.28 mmol/g. Based on thermal analysis it was shown, that sample annealed in nitrogen atmosphere is the most thermally stable material. In turn, according to the results obtained both from photoacoustic spectroscopy and mass spectroscopy, samples subjected to oxidation with HNO3 or H2O2 followed by heat treatment with using of microwave radiation are characterised by the highest content of oxygen functional groups.


Activated carbons Nitrogenation Oxidation Microwave heating Thermal analysis Photoacoustic spectroscopy 

1 Introduction

In recent time, much attention has been devoted to modified carbonaceous materials because of a huge spectrum of their applications in various branches of industry as well as everyday life. Such materials can be used not only as adsorbents of gaseous and liquid impurities, but also as catalyst, catalysts supports as well as electrode materials for electrochemical capacitors and lithium-ion batteries (Huang et al. 2006; Severa et al. 2018; Zaini et al. 2010, Su et al. 2018; Liang et al. 2004; Nowicki and Pietrzak 2011; Chen et al. 2003). The physicochemical properties of such materials depend in significant degree on the quantity and type of heteroatomic functional groups introduced into the carbon matrix by means of different modification. Through introduction of nitrogen, oxygen or sulphur functional species into carbonaceous materials structure is possible to change in large extent their acidic–basic, hydrophobic–hydrophilic character as well as their sorption, catalytic or thermal properties. The effects of functionalization of different carbonaceous materials have been widely reported in many papers (López et al. 2003; Kazmierczak-Razna et al. 2015; Nowicki et al. 2015; Nowicki 2016; Ternero-Hidalgo et al. 2016; Gokce and Aktas 2014; Bhatnagar et al. 2013).

In general, preparation of modified activated carbons is based on conventional heating, which has many drawbacks. An interesting alternative is the use of microwave radiation for this purpose, which is based on conversion of electromagnetic energy into thermal energy. In contrast to conventional method, microwave-assisted heating is faster, safer, easier to control and takes place in the entire volume of the sample, so ensures uniform heating of material and accelerates the course of modification process. Taking it into consideration, the main aim of this study was preparation and physicochemical characterization of new carbonaceous materials, obtained by means of nitrogenation, oxidation and thermal treatment of peat-based activated carbon with the use of microwave heating. In order to fully characterize the obtained materials except for obvious ash content analysis, elemental composition of the starting and modified activated carbons, characterization of the pore structure and pH measurements, coupled method TG/MS (thermogravimetry/mass spectroscopy) and photoacoustic spectroscopy was used.

2 Experimental

2.1 Preparation of modified activated carbons

At the beginning, the starting peat was subjected to pyrolysis in a quartz tubular reactor heated by horizontal furnace, under a stream of nitrogen blown at the rate of 0.170 L/min. The sample was heated (10°C/min) from room temperature to the final pyrolysis temperature of 600 °C and maintained for 60 min. After that the obtained char was subjected to physical activation with steam at 800 °C, for 60 min. In order to obtain materials characterised by diverse functional groups content (both in terms of the type and quantity) such prepared activated carbon (denoted as A) was next subjected to four different treatment: (1) oxidation with boiling 25% solution of nitric acid for 3 h followed by heat treatment at 600 °C for 30 min (denoted as AN), (2) oxidation with 30% solution of hydrogen peroxide at room temperature for 3 h followed by heat treatment at 600 °C for 30 min (denoted as AH), (3) annealing in nitrogen atmosphere at 900 °C for 30 min (denoted as AT) and (4) impregnation with urea (at the weight ratio of 1:1) followed by heat treatment at 800 °C for 30 min (denoted as AU). All the modifications were carried out in a porcelain crucibles heated by microwave muffle furnace Phoenix, provided by CEM Corporation (United States).

2.2 Sample characterisation

The ash content for all materials under investigation was determined according to the DNS ISO 1171:2002 standard. Elemental composition of the starting and modified activated carbons was determined using the CHNS Vario EL III analyser (Elementar Analysensysteme GmbH, Germany), whereas the oxygen content was calculated by the difference. Characterization of the pore structure of activated carbons was based on the nitrogen adsorption–desorption measured at − 196 °C on Autosorb iQ surface area analyser (Quantachrome Instruments, United States). Prior to the isotherm measurements, the samples were out-gassed at 300 °C for 8 h. BET specific surface area (SBET) was evaluated in the range of relative pressures p/p0 of 0.05–0.30. Total pore volume (Vt) was calculated by converting the amount adsorbed at p/p0 ~ 0.99 to the volume of liquid adsorbate. Average pore diameter (D) was calculated from equation D = 4Vt/SBET. Pore size distribution was calculated from the adsorption branches of isotherms, using the BJH method. Micropore volume (Vm) and area (Smicro) were determined by the t-plot method. To estimate the content of surface functional groups of acidic and basic character the Boehm method was applied (Boehm 1994). The pH measurement was performed using an pH-meter manufactured by Metrohm Ion Analysis (Switzerland), equipped in combined glass pH electrode with temperature sensor (Unitrode Pt1000), calibrated with standards solutions of pH 3, 7 and 10.

Thermal analysis was carried out on a STA 449 Jupiter F1 (Netzsch, Germany) under the following operational conditions: heating rate 10°C/min, the dynamic atmosphere of helium (50 ml/ min) in the temperature range of 25–1000 °C, sample mass of about 5 mg, sensor thermocouple type S TG-DTA. As a reference, empty Al2O3 crucible was used. The volatile products coming out during decomposition process were detected by quadrupole mass spectrometer QMS 403C Aëolos (Netzsch, Germany) coupled on-line to STA instrument. The mass spectrometer was connected on-line to STA instrument by quartz capillary heated to 300 °C. The QMS was operated with an electron impact ionizer with energy 70 eV. The measurements performed in scan mode for m/z, where m is the mass of molecule and z is a charge of the molecule in electron charge units in the range from 10 to 110 amu allowed to identify all possible volatile particles produced during the decomposition.

The photoacoustic (PAS) spectra were recorded by means of Bio-Rad Excalibur FT-IR 3000 MX spectrometer equipped in with MTEC Model 300 photoacoustic cell, over the 4000–400 cm− 1 range at room temperature, resolution 4 cm− 1 and maximum source aperture. Dry helium was used to purge the PAS cell before data collection. The spectrum was normalized by computing the ratio of a sample spectrum to the spectrum of a MTEC carbon black standard. A stainless steel cup (diameter 10 mm) was filled with sample (thickness < 6 mm). Interferograms of 1024 scans were averaged for the spectrum, providing good signal-to-noise (S/N) ratio. All samples were dried in 115 °C for 48 h.

3 Results and discussion

As follow from the data presented in Table 1 the starting peat-based activated carbon is characterised by very high Cdaf content (94.3 wt%), relatively high amount of mineral matter (7.5 wt%) and small admixture of non-carbon organic components, mainly oxygen. As seen, each of the modifications carried out caused significant changes in the chemical composition of starting material. These changes are most evident in case of AU and AN samples. Sample prepared by reaction with urea followed by thermal treatment at 800 °C (AU) shows the highest nitrogen and simultaneously the lowest oxygen content among the investigated carbon materials. In turn, in structure of AN sample (prepared by means of nitric acid oxidation followed by heat treatment at 600 °C), the lowest carbon content and the highest contribution of oxygen was found. Other variants of thermo-chemical treatment cause a slight increase in the Cdaf contribution and slight changes in the content of hydrogen and heteroatoms. These changes are most probably a consequence of gasification of least stable fragments of carbonaceous structure as well as progressing aromatisation of carbon matrix during heat treatment.

Table 1

Elemental composition of activated carbons (wt%)











































daf dry-ash-free basis, diff calculated by difference

According to the data presented in Table 2 all modifications lead also to significant changes in acid-base properties of the peat-based activated carbon. As a result of thermo-chemical treatment the total content of surface functional groups increase, in particular for AN sample, which contain almost three times more groups of acidic character as well as twice more basic surface groups than unmodified carbon (A). In turn, the AT sample, received by means of annealing of starting activated carbon in nitrogen atmosphere is characterised by the highest content (0.93 mmol/g) and simultaneously the greatest prevalence of basic functional groups (almost five times) over acidic ones, what is also confirmed by very high pH value (10.57). This is most probably a consequence of high temperature of annealing (900 °C), which favours formation of greater amount of functional groups of basic nature as well as leads to a decomposition of the majority of acidic groups present on carbon surface. In case of samples subjected to thermal treatment in milder conditions (AH, AU and especially AN) the dominance of basic functional groups is definitely smaller.

Table 2

Acidic-basic properties of the activated carbons



Acidic groups (mmol/g)

Basic groups (mmol/g)

Total content (mmol/g)


























As indicated by the data collected in Table 3 and in Figs. 1 and 2, all the samples under investigation show very similar textural parameters, independent on variant of modification. They have medium-developed surface area ranging from 582 to 657 m2/g and porous structure with dominant mesopores. The most developed surface area of 657 m2/g was found for sample AN oxidised with HNO3 and subjected to thermal treatment in microwave furnace at 600 °C, while the greatest total pore volume of 0.78 cm3/g as well as the most mesoporous character of texture was found for unmodified activated carbon (A). As follows from further analysis of the textural data, modification of starting activated carbon led to generation of some new micropores in its porous structure. This process is most effective in case of AN and AT samples, for which the micropore contribution in total pore volume is by 7 and 4% higher than for unmodified carbon. It is also confirmed by narrower average pore diameter in comparison to AH, AU and particularly to starting activated carbon.

Table 3

Textural parameters of activated carbons


Surface area (m2/g)

Pore volume (cm3/g)


D (nm)








































Vm/Vt, micropore contribution

Fig. 1

Nitrogen adsorption/desorption isotherms of the activated carbons

Fig. 2

Pore size distribution of the activated carbons

According to the IUPAC classification, the isotherms obtained for all prepared carbons (Fig. 1) belong to type IV, which is characteristic for micro/mesoporous materials. In the range of relative pressure between 0 and ~ 0.45 the adsorption branch of isotherm increase slowly, what indicates the mono- and multi-molecular layer sorption in micro and mesopores. Further increase of relative pressure causes a capillary condensation in mesopores, what is evidenced by wide hysteresis loop, similar to H3 type. In turn, the lack of the horizontal plateau as well as a rapid increase in adsorption capacity at p/p0 close to 1, suggest that the samples studied have also some amount of macropores. As follows from the course of pore size distribution curves presented in Fig. 2, the main contribution in the porous structure of carbons studied have mesopores with diameters in the range between 3 and 12 nm.

All tested samples were subjected also to thermal and spectroscopic analysis. By using coupled methods, we can get in one analysis, multiple data. Based on thermal studies we get information about thermal stability, how the mass loss is changing during the temperature increase and based on the curve slop we can estimate the tendency of the samples degradation. Activated carbon obtained via physical activation of peat with steam at 800 °C—sample A—is thermally stable up to 545 °C (recorded mass loss 2.5 wt%). Sample AU, which was subjected to impregnation with urea followed by heat treatment at 800 °C has almost identical thermal stability (Figs. 3, 4). Annealing in nitrogen atmosphere at 900 °C or subjecting sample A to oxidation with 25% solution of nitric acid followed by heat treatment at 600 °C enhance the thermal stability, while oxidation with 30% solution of hydrogen peroxide followed by heat treatment at 600 °C diminishes it. But, it should be noted that sample AN, after reaching temperature of 580 °C (recorded mass loss of 2.4 wt%) begins to lose mass very quickly. Nevertheless, the sample annealed in nitrogen atmosphere (AT) is the most stable sample. This is most likely related to the incorporation of nitrogen atoms into the surface carbon layers. Carbons with built-in nitrogen atoms have greater thermal stability (Jankowska et al. 1991). When discussing thermal stability, one should take into account the changes that occur at the beginning of the temperature rise. Figures 5 and 6 shows the changes of intensity of ions m:17 and m:18 which are responsible to the presence of hydroxyl groups and water. Their presence are also visible on Fig. 4, where observed maximum on DTG curves around 40 °C is due to the desorption of the physically absorbed water. By subjecting the material to oxidation process, its surface will acquire a strong hydrophilic character, which will cause strong water sorption. As it shown in Table 1 sample AN is characterized by a high oxygen content, which is also confirmed by MS spectroscopy (Figs. 5, 6) by relatively high content of water and hydroxyl groups. It should be also noted that in the case of sample AU (which was subjected to impregnation with urea), the presence of ions: 17 and 18 can also suggest the presence of ammonia and ammonium.

Fig. 3

TG curves of the activated carbons

Fig. 4

DTG curves of the activated carbons

Fig. 5

Temperature distribution of ion m:17

Fig. 6

Temperature distribution of ion m:18

By looking at the Figs. 3 and 4 it can be certainly stated that the sample AH has the lowest thermal stability. At the very beginning of the temperature rise, a large mass loss of 3.3 wt% till 190 °C is noticeable (DTG curve maximum recorded at 100 °C). At this temperature, the mass loss is no longer so rapid. This mass loss is not only related to the presence to ions: 17 and 18 but also to the presence to ions: 29, 41, 42, 43 (which are only recorded for this sample) (Fig. 7). These ions are most likely responsible for the presence of the following groups: CHO, CH3CN, NCO(+H). Presented data indicate, that the carbon surface was successfully oxidized. Based on data collected in Fig. 8 it can be concluded, that all tested sample around temperature of 525 °C starts to emit ion: 44, which probably is responsible for the presence of carboxyl group.

Fig. 7

Temperature distribution of ions m: 29, 41, 42, 43 for sample AH

Fig. 8

Temperature distribution of ion m: 44

The FT-IR spectra of the samples in the region of C–H and –OH groups are presented in Fig. 9. There are no bands indicating the presence of C–H (–CH2 or –CH3) groups in the carbon material. The intense band in the 2400–2300 cm− 1 range indicates the presence of the carbonization product, namely carbon dioxide, which is probably trapped in the carbon structure and not removed during drying. The band of CO2 is visible also in 700–600 cm− 1 range (peak at ~ 680 cm− 1, Fig. 10), but only in AT, AH and AN samples spectra. In the case of other samples, the peak of CO2 is inverse (2400–2300 cm− 1) and there is no peak visible at ~ 680 cm− 1. This is probably due to the fact that there is less CO2 remained in the pores of these carbon samples that is in carbon black standard (used for background collection).

Fig. 9

FT-IR/PAS spectra of examined samples in the 3500–2000 cm− 1 range

Fig. 10

FT-IR/PAS spectra of examined samples in the 1400–400 cm− 1 range

The fingerprint region is the most suitable for oxygen groups identification (Fig. 10), although all bands in this region have relatively low intensity. Region below 1300 cm− 1 is difficult to interpret in detail because C–O stretching modes (ethers, esters, alcohols), as well as C–OH bending modes (alcohols, amides) absorb in the same frequency range. The bands below 1050 cm− 1 may also have inorganic compounds contribution (i.e. silica and other inorganic compounds), which is caused by their presence in the starting material (peat moss). These modes are coupled with other vibrations and do not exhibit well defined group frequencies (Bellamy 1980). Some assignments are nevertheless possible. The bands at 1218, 1145, 1084, 570, 535 and 495 cm− 1 could be due to C–O and C–O–C in ether structures and/or C=C stretching in aromatic structures (C–C skeleton vibrations) (Gomez-Serrano et al. 1999). The intensities of those peaks are the lowest in the case of A and AU samples. The band at ~ 930 cm− 1, absent in A and AU samples, may be attributed to N–O stretching in oximes or out-of-plane deformation vibration in –COOH groups (Socrates 2001). Additional band at 1461 cm− 1, which is present only in AH sample spectra, indicate the presence of C–C=O in-plane deformation vibration of –COOH groups present on the samples surface (Socrates 2001). Unfortunately, this cannot be confirmed by analysing the spectra above 1400 cm− 1 (not shown) due to the wide, ragged band in the range of 1450–1850 cm− 1 (hydrogen bonded O–H stretching vibrations; unremoved water). The PAS spectra have also inverse peaks (about 1050–1000 cm− 1), the presence of which is probably due to the fact that the carbon black standard used for normalizing the PAS spectra has higher intensity of bands in this range than the analysed sample. Nevertheless, the presence of oxygen functional groups in analysed region indicates that the modification with oxidizing agents was effective, although the amount of these groups is very small, most probably as a consequence of further thermal treatment in microwave furnace.

4 Conclusions

The above-discussed results have proved that, application of different variants of peat-based activated carbon, such as oxidation, nitrogenation and high temperature treatment with the use of microwave energy, allows to produce a wide panoply of carbonaceous materials, differing significantly in the type of porous structure, chemical composition as well as acid-base character of surface. Moreover, it has been proved that the functional groups introduced into activated carbon structure affect in very high extent its thermal stability. Annealing of the activated carbon in nitrogen atmosphere at 900 °C or oxidation with 25% solution of nitric acid followed by heat treatment at 600 °C enhance the thermal stability of carbonaceous structure, whereas the oxidation with 30% solution of hydrogen peroxide followed by heat treatment at 600 °C diminishes it. Based on both mass and photoacoustic spectroscopy the introduction of oxygen functional groups has been proven.



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Authors and Affiliations

  1. 1.Laboratory of Optical Fibers Technology, Faculty of ChemistryMaria Curie-Sklodowska UniversityLublinPoland
  2. 2.Department of Chemical Technology, Faculty of ChemistryMaria Curie-Sklodowska UniversityLublinPoland
  3. 3.Laboratory of Applied Chemistry, Faculty of ChemistryAdam Mickiewicz University in PoznańPoznańPoland

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