Preparation of biomass carbon material based on Fomes fomentarius via alkali activation and its application for the removal of brilliant green in wastewater
“…As the temperature continued to rise to 500 °C, the samples showed a dramatic weight loss, which could be explained by the high temperature decomposition of the oxygenated components of CD (fat, protein, and lignocellulose, etc.) into tar and combustible gases [ 26 ]. However, when the temperature exceeds 500 °C, the curve becomes stable without further weight loss, indicating that the carbonization process is complete.…”
Section: Resultsmentioning
confidence: 99%
“…FT-IR were used to investigate the functional groups of the materials, and the results were shown in Figure 2 A. The broadband corresponding to the -OH stretching vibration of hydroxyl functional groups in the range of 3450–3410 cm −1 is still existed, showing the existence of residual oxygen-containing functional groups on the resultant biochar materials [ 25 , 26 ]. The CDC and BMCDs had weaker -CH bonds (2910–2930 cm −1 , -CH group’s symmetric and asymmetric stretching vibration peaks) than the CD, indicating that a considerable quantity of hydrogen was removed during the carbonization and activation procedures [ 27 ].…”
Section: Resultsmentioning
confidence: 99%
“…N 2 adsorption-desorption isotherms were used to obtain the specific surface areas and porosity of the biochar materials, the results were shown as Figure 3 and Table 1 . As can be seen from the inset of Figure 3 A, the specific surface area and the total pore volume of CDC (23.8 m 2 g −1 , 0.0436 cm 3 g −1 ) have been increased relative to that of CD (0.9 m 2 g −1 , 0.0071 cm 3 g −1 ) after carbonization, which may be caused by high-temperature pyrolysis [ 25 , 26 ]. It is worth noting that CDC is not sufficient to support the excellent performance of CD-based on these results; thus, further activation is required to improve the specific surface area and pore volume.…”
Section: Resultsmentioning
confidence: 99%
“…Like many biochars [ 32 , 33 , 34 ], BMCDs also contain mainly C, O, and N elements ( Figure 4 ). The high-resolution C1s spectrum of the BMCDs showed four peaks, with the typical peaks at 283.91–284.15 eV corresponding to C-C, 285.23–285.69 eV corresponding to C-O, 286.82 eV corresponding to C=O, and 288.20 eV corresponding to O-C=C [ 25 , 26 ]. The high-resolution O1s spectrum of the BMCDs showed three peaks, with the typical peaks at 530.42 eV corresponding to quinones, 531.38 eV corresponding to C=O, 532.10–532.68 eV corresponding to C-O, and 534.13–534.79 eV corresponding to O-H [ 25 , 26 ].…”
Section: Resultsmentioning
confidence: 99%
“…The high-resolution C1s spectrum of the BMCDs showed four peaks, with the typical peaks at 283.91–284.15 eV corresponding to C-C, 285.23–285.69 eV corresponding to C-O, 286.82 eV corresponding to C=O, and 288.20 eV corresponding to O-C=C [ 25 , 26 ]. The high-resolution O1s spectrum of the BMCDs showed three peaks, with the typical peaks at 530.42 eV corresponding to quinones, 531.38 eV corresponding to C=O, 532.10–532.68 eV corresponding to C-O, and 534.13–534.79 eV corresponding to O-H [ 25 , 26 ]. The high-resolution N1s spectrum of the BMCDs showed two peaks, with the typical peaks at 398.08–399.52 eV corresponding to pyridinic-N and 400.10–400.95 eV corresponding to pyrrolic-N [ 33 ].…”
Cow dung (CD) is a waste product of livestock production. Improper disposal of a large amount of CD will cause environmental pollution. In this work, three biochar materials based on CD (BMCD) were prepared by using three types of base, including KOH, NaOH, and mixed base (MB, a mixture of equal mass NaOH and KOH) as activators to investigate the different physicochemical properties of BMCDs (BMCD-K, BMCD-Na, and BMCD-MB). The objective was to verify the effectiveness of MB activation in the preparation of biochar materials. The results show that MB has an effect on the structural characteristics of BMCDs. In particular, the surface area and total pore volume, the specific surface area, and the total pore volume of BMCD-MB (4081.1 m2 g−1 and 3.0118 cm3 g−1) are significantly larger than those of BMCD-K (1784.6 m2 g−1 and 1.1142 cm3 g−1) and BMCD-Na (1446.1 m2 g−1 and 1.0788 cm3 g−1). While synthetic dye rhodamine B (RhB) and antibiotic tetracycline hydrochloride (TH) were selected as organic pollutant models to explore the adsorption performances, the maximum adsorption capacities of BMCD-K, BMCD-NA and BMCD-MB were 951, 770, and 1241 mg g−1 for RhB, 975, 1051, and 1105 mg g−1 for TH, respectively, which were higher than those of most adsorbents. This study demonstrated that MB can be used as an effective activator for the preparation of biochar materials with enhanced performance.
“…As the temperature continued to rise to 500 °C, the samples showed a dramatic weight loss, which could be explained by the high temperature decomposition of the oxygenated components of CD (fat, protein, and lignocellulose, etc.) into tar and combustible gases [ 26 ]. However, when the temperature exceeds 500 °C, the curve becomes stable without further weight loss, indicating that the carbonization process is complete.…”
Section: Resultsmentioning
confidence: 99%
“…FT-IR were used to investigate the functional groups of the materials, and the results were shown in Figure 2 A. The broadband corresponding to the -OH stretching vibration of hydroxyl functional groups in the range of 3450–3410 cm −1 is still existed, showing the existence of residual oxygen-containing functional groups on the resultant biochar materials [ 25 , 26 ]. The CDC and BMCDs had weaker -CH bonds (2910–2930 cm −1 , -CH group’s symmetric and asymmetric stretching vibration peaks) than the CD, indicating that a considerable quantity of hydrogen was removed during the carbonization and activation procedures [ 27 ].…”
Section: Resultsmentioning
confidence: 99%
“…N 2 adsorption-desorption isotherms were used to obtain the specific surface areas and porosity of the biochar materials, the results were shown as Figure 3 and Table 1 . As can be seen from the inset of Figure 3 A, the specific surface area and the total pore volume of CDC (23.8 m 2 g −1 , 0.0436 cm 3 g −1 ) have been increased relative to that of CD (0.9 m 2 g −1 , 0.0071 cm 3 g −1 ) after carbonization, which may be caused by high-temperature pyrolysis [ 25 , 26 ]. It is worth noting that CDC is not sufficient to support the excellent performance of CD-based on these results; thus, further activation is required to improve the specific surface area and pore volume.…”
Section: Resultsmentioning
confidence: 99%
“…Like many biochars [ 32 , 33 , 34 ], BMCDs also contain mainly C, O, and N elements ( Figure 4 ). The high-resolution C1s spectrum of the BMCDs showed four peaks, with the typical peaks at 283.91–284.15 eV corresponding to C-C, 285.23–285.69 eV corresponding to C-O, 286.82 eV corresponding to C=O, and 288.20 eV corresponding to O-C=C [ 25 , 26 ]. The high-resolution O1s spectrum of the BMCDs showed three peaks, with the typical peaks at 530.42 eV corresponding to quinones, 531.38 eV corresponding to C=O, 532.10–532.68 eV corresponding to C-O, and 534.13–534.79 eV corresponding to O-H [ 25 , 26 ].…”
Section: Resultsmentioning
confidence: 99%
“…The high-resolution C1s spectrum of the BMCDs showed four peaks, with the typical peaks at 283.91–284.15 eV corresponding to C-C, 285.23–285.69 eV corresponding to C-O, 286.82 eV corresponding to C=O, and 288.20 eV corresponding to O-C=C [ 25 , 26 ]. The high-resolution O1s spectrum of the BMCDs showed three peaks, with the typical peaks at 530.42 eV corresponding to quinones, 531.38 eV corresponding to C=O, 532.10–532.68 eV corresponding to C-O, and 534.13–534.79 eV corresponding to O-H [ 25 , 26 ]. The high-resolution N1s spectrum of the BMCDs showed two peaks, with the typical peaks at 398.08–399.52 eV corresponding to pyridinic-N and 400.10–400.95 eV corresponding to pyrrolic-N [ 33 ].…”
Cow dung (CD) is a waste product of livestock production. Improper disposal of a large amount of CD will cause environmental pollution. In this work, three biochar materials based on CD (BMCD) were prepared by using three types of base, including KOH, NaOH, and mixed base (MB, a mixture of equal mass NaOH and KOH) as activators to investigate the different physicochemical properties of BMCDs (BMCD-K, BMCD-Na, and BMCD-MB). The objective was to verify the effectiveness of MB activation in the preparation of biochar materials. The results show that MB has an effect on the structural characteristics of BMCDs. In particular, the surface area and total pore volume, the specific surface area, and the total pore volume of BMCD-MB (4081.1 m2 g−1 and 3.0118 cm3 g−1) are significantly larger than those of BMCD-K (1784.6 m2 g−1 and 1.1142 cm3 g−1) and BMCD-Na (1446.1 m2 g−1 and 1.0788 cm3 g−1). While synthetic dye rhodamine B (RhB) and antibiotic tetracycline hydrochloride (TH) were selected as organic pollutant models to explore the adsorption performances, the maximum adsorption capacities of BMCD-K, BMCD-NA and BMCD-MB were 951, 770, and 1241 mg g−1 for RhB, 975, 1051, and 1105 mg g−1 for TH, respectively, which were higher than those of most adsorbents. This study demonstrated that MB can be used as an effective activator for the preparation of biochar materials with enhanced performance.
With the development of economy and increasing environmental awareness, how to effectively remove organic pollutants in wastewater is a research hotspot. Adsorption is one of the effective methods, and the adsorption material is the key factor to determine the efficiency. In this review, biomass‐derived carbon materials as adsorbents of organic pollutants and the adsorption mechanism are discussed in depth. The effects of carbonization and activation on the morphology and structure of carbon materials; the modification strategies of carbon adsorbents, the adsorption performance of biomass‐derived carbon materials for organic pollutants are described and illustrated; the future work of the biomass‐derived carbon materials is proposed.
In this study, a novel electrochemical sensor was developed for the detection of baicalein based on multi-walled carbon nanotube (MWCNT) and banana peel derived biomass carbon (BPBC) composite modified glassy carbon electrode (GCE). The BPBC was synthesized by carbonization and alkali activation method using commonly available banana peel as the raw material, which was further mixed with MWCNT to obtain BPBC-MWCNT composite. Then the composite modified GCE was fabricated and used for voltammetric detection of baicalein with a wide detection range from 0.0040 to 100.0 μM as well as a low detection limit of 1.33 nM (3σ/S). Also, the electrochemical behaviors of baicalein on BPBC-MWCNT/GCE were investigated by cyclic voltammetry in detail. The proposed method was applied to the detection of baicalein content in Shuanghuanglian oral liquid with satisfactory results. Therefore, this work extended the electrochemical method for the drug analysis by using biomassderived carbon-based composite.
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