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CIVIL & ENVIRONMENTAL ENGINEERING

Binary adsorption studies of Cr(VI) and Cu(II) ions from synthetic wastewater using carbon from Feoniculum vulgare (fennel seeds)

ORCID Icon, ORCID Icon, ORCID Icon & ORCID Icon
Article: 2119530 | Received 28 Aug 2021, Accepted 28 Aug 2022, Published online: 08 Sep 2022

Figures & data

Figure 1. XRD graphs for (a) FS-500, FS-600 & FS-700; (b) KMFS-500, KMFS-600 & KMFS-700.

Figure 1. XRD graphs for (a) FS-500, FS-600 & FS-700; (b) KMFS-500, KMFS-600 & KMFS-700.

Figure 2. FTIR spectra for (a) FS-500, FS-600 and fs-700 and (b) KMFS-500, KMFS-600 and KNFS-700.

Figure 2. FTIR spectra for (a) FS-500, FS-600 and fs-700 and (b) KMFS-500, KMFS-600 and KNFS-700.

Figure 3. SEM and EDX results for (a) FS-500, (b) FS-600, (c) FS-700, (d) KMFS-500, (e) KMFS-600 and (f) KMFS-700.

Figure 3. SEM and EDX results for (a) FS-500, (b) FS-600, (c) FS-700, (d) KMFS-500, (e) KMFS-600 and (f) KMFS-700.

Figure 4. UV-Vis results for (a) FS-500, FS-600 and FS-700; (b) KMFS-500, KMFS-600 and KMFS-700.

Figure 4. UV-Vis results for (a) FS-500, FS-600 and FS-700; (b) KMFS-500, KMFS-600 and KMFS-700.

Table 1. Point zero charge pH(PZC) of the adsorbent

Figure 5. Effect of concentration for the removal of Cu(II) on (a) FS-500, FS-600 and FS-700; (b) Cr(VI) on FS-500, FS-600; (c) Cu(II) on KMFS-500, KMFS-600 and KMFS-700 and Cr(VI) (d) KMFS-500, KMFS-600 and KMFS-700.[Conditions: pH(5), adsorbent dosage (0.1 g), contact time (2 h), solution volume (20 mL), temperature (298 K) and agitation speed(200 rpm)].

Figure 5. Effect of concentration for the removal of Cu(II) on (a) FS-500, FS-600 and FS-700; (b) Cr(VI) on FS-500, FS-600; (c) Cu(II) on KMFS-500, KMFS-600 and KMFS-700 and Cr(VI) (d) KMFS-500, KMFS-600 and KMFS-700.[Conditions: pH(5), adsorbent dosage (0.1 g), contact time (2 h), solution volume (20 mL), temperature (298 K) and agitation speed(200 rpm)].

Figure 6. Effect of time for the removal of Cu(II) on (a) FS-500, FS-600 and FS-700; (b) Cr(VI) on FS-500, FS-600; (c) Cu(II) on KMFS-500, KMFS-600 and KMFS-700 and Cr(VI) (d) KMFS-500, KMFS-600 and KMFS-700. [Conditions: pH(5), adsorbent dosage (0.1 g), concentration (100 mg/L, solution volume (20 mL), temperature (298 K) and agitation speed(200 rpm)].

Figure 6. Effect of time for the removal of Cu(II) on (a) FS-500, FS-600 and FS-700; (b) Cr(VI) on FS-500, FS-600; (c) Cu(II) on KMFS-500, KMFS-600 and KMFS-700 and Cr(VI) (d) KMFS-500, KMFS-600 and KMFS-700. [Conditions: pH(5), adsorbent dosage (0.1 g), concentration (100 mg/L, solution volume (20 mL), temperature (298 K) and agitation speed(200 rpm)].

Figure 7. Effect of temperature for the removal of Cu(II) on (a) FS-500, FS-600 and FS-700; (b).

Figure 7. Effect of temperature for the removal of Cu(II) on (a) FS-500, FS-600 and FS-700; (b).

Figure 8. Effect of pH for the removal of Cu(II) on (a) FS-500, FS-600 and FS-700; (b) Cr(VI) on FS-500, FS-600; (c) Cu(II) on KMFS-500, KMFS-600 and KMFS-700 and Cr(VI) (d) KMFS- 500, KMFS-600 and KMFS-700. [Conditions: temperature (298 K), adsorbent dosage (0.1 g), concentration (100 mg/L, solution volume (20 mL), time (2 h) and agitation speed (200 rpm)].

Figure 8. Effect of pH for the removal of Cu(II) on (a) FS-500, FS-600 and FS-700; (b) Cr(VI) on FS-500, FS-600; (c) Cu(II) on KMFS-500, KMFS-600 and KMFS-700 and Cr(VI) (d) KMFS- 500, KMFS-600 and KMFS-700. [Conditions: temperature (298 K), adsorbent dosage (0.1 g), concentration (100 mg/L, solution volume (20 mL), time (2 h) and agitation speed (200 rpm)].

Table 2. Adsorption kinetics studies for carbonized fennel seeds

Table 3. Adsorption kinetics studies for KMnO4 treated carbonized fennel seeds

Table 4. Adsorption isotherms studies for carbonized fennel seeds

Table 5. Adsorption isotherms studies for KMnO4 treated carbonized fennel seeds

Table 6. Adsorption thermodynamic studies for carbonized fennel seeds

Table 7. Comparison with other adsorbents

Figure 9. Reusability studies for (a) Cu(II) and (b) Cr(VI) on carbonized fennel seeds and (c) Cu(II) and (d) Cr(VI) on KMnO4 treated carbonized fennel seeds. Mechanism for Cr(VI) and Cu(II).

Figure 9. Reusability studies for (a) Cu(II) and (b) Cr(VI) on carbonized fennel seeds and (c) Cu(II) and (d) Cr(VI) on KMnO4 treated carbonized fennel seeds. Mechanism for Cr(VI) and Cu(II).

Figure 10. Schematic diagram for the adsorption mechanism of Cr(VI) and Cu(II) on the adsorbents surface.

Figure 10. Schematic diagram for the adsorption mechanism of Cr(VI) and Cu(II) on the adsorbents surface.

Figure 11. FTIR spectra for Cu(II) and Cr(VI) on FS-600 and KMFS-700 before and after adsorption.

Figure 11. FTIR spectra for Cu(II) and Cr(VI) on FS-600 and KMFS-700 before and after adsorption.

Figure 12. SEM images and EDX results for (a) FS-500, (b) FS-600, (c) FS-700. (d) KMFS-500, (e) KMFS-600 and (f) KMFS-700 after adsorption.

Figure 12. SEM images and EDX results for (a) FS-500, (b) FS-600, (c) FS-700. (d) KMFS-500, (e) KMFS-600 and (f) KMFS-700 after adsorption.

Data availability statement

The data supporting the findings of the study may be made available from the corresponding authors on request.