Cow bones char as a green sorbent for fluorides removal from aqueous solutions: batch and fixed-bed studies

Cow bone char was investigated as sorbent for the defluoridation of aqueous solutions. The cow bone char was characterized in terms of its morphology, chemical composition, and functional groups present on the bone char surface using different analytical techniques: SEM, EDS, N 2 -BET method, and FT...

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Veröffentlicht in:Environmental science and pollution research international 2017, Vol.24 (3), p.2364-2380
Hauptverfasser: Nigri, Elbert M., Cechinel, Maria Alice. P., Mayer, Diego A., Mazur, Luciana. P., Loureiro, José M., Rocha, Sônia D. F., Vilar, Vítor J. P.
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container_issue 3
container_start_page 2364
container_title Environmental science and pollution research international
container_volume 24
creator Nigri, Elbert M.
Cechinel, Maria Alice. P.
Mayer, Diego A.
Mazur, Luciana. P.
Loureiro, José M.
Rocha, Sônia D. F.
Vilar, Vítor J. P.
description Cow bone char was investigated as sorbent for the defluoridation of aqueous solutions. The cow bone char was characterized in terms of its morphology, chemical composition, and functional groups present on the bone char surface using different analytical techniques: SEM, EDS, N 2 -BET method, and FTIR. Batch equilibrium studies were performed for the bone chars prepared using different procedures. The highest sorption capacities for fluoride were obtained for the acid washed ( q  = 6.2 ± 0.5 mg/g) and Al-doped ( q  = 6.4 ± 0.3 mg/g) bone chars. Langmuir and Freundlich models fitted well the equilibrium sorption data. Fluoride removal rate in batch system is fast in the first 5 h, decreasing after this time until achieving equilibrium due to pore diffusion. The presence of carbonate and bicarbonate ions in the aqueous solution contributes to a decrease of the fluoride sorption capacity of the bone char by 79 and 31 %, respectively. Regeneration of the F-loaded bone char using 0.5 M NaOH solution leads to a sorption capacity for fluoride of 3.1 mg/g in the second loading cycle. Fluoride breakthrough curve obtained in a fixed-bed column presents an asymmetrical S -shaped form, with a slow approach of C / C 0  → 1.0 due to pore diffusion phenomena. Considering the guideline value for drinking water of 1.5 mg F − /L, as recommended by World Health Organization, the service cycle for fluoride removal was of 71.0 h ([F − ] feed  ∼ 9 mg/L; flow rate = 1 mL/min; m sorbent  = 12.6 g). A mass transfer model considering the pore diffusion was able to satisfactorily describe the experimental data obtained in batch and continuous systems.
doi_str_mv 10.1007/s11356-016-7816-5
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P. ; Mayer, Diego A. ; Mazur, Luciana. P. ; Loureiro, José M. ; Rocha, Sônia D. F. ; Vilar, Vítor J. P.</creator><creatorcontrib>Nigri, Elbert M. ; Cechinel, Maria Alice. P. ; Mayer, Diego A. ; Mazur, Luciana. P. ; Loureiro, José M. ; Rocha, Sônia D. F. ; Vilar, Vítor J. P.</creatorcontrib><description>Cow bone char was investigated as sorbent for the defluoridation of aqueous solutions. The cow bone char was characterized in terms of its morphology, chemical composition, and functional groups present on the bone char surface using different analytical techniques: SEM, EDS, N 2 -BET method, and FTIR. Batch equilibrium studies were performed for the bone chars prepared using different procedures. The highest sorption capacities for fluoride were obtained for the acid washed ( q  = 6.2 ± 0.5 mg/g) and Al-doped ( q  = 6.4 ± 0.3 mg/g) bone chars. Langmuir and Freundlich models fitted well the equilibrium sorption data. Fluoride removal rate in batch system is fast in the first 5 h, decreasing after this time until achieving equilibrium due to pore diffusion. The presence of carbonate and bicarbonate ions in the aqueous solution contributes to a decrease of the fluoride sorption capacity of the bone char by 79 and 31 %, respectively. Regeneration of the F-loaded bone char using 0.5 M NaOH solution leads to a sorption capacity for fluoride of 3.1 mg/g in the second loading cycle. Fluoride breakthrough curve obtained in a fixed-bed column presents an asymmetrical S -shaped form, with a slow approach of C / C 0  → 1.0 due to pore diffusion phenomena. Considering the guideline value for drinking water of 1.5 mg F − /L, as recommended by World Health Organization, the service cycle for fluoride removal was of 71.0 h ([F − ] feed  ∼ 9 mg/L; flow rate = 1 mL/min; m sorbent  = 12.6 g). 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The highest sorption capacities for fluoride were obtained for the acid washed ( q  = 6.2 ± 0.5 mg/g) and Al-doped ( q  = 6.4 ± 0.3 mg/g) bone chars. Langmuir and Freundlich models fitted well the equilibrium sorption data. Fluoride removal rate in batch system is fast in the first 5 h, decreasing after this time until achieving equilibrium due to pore diffusion. The presence of carbonate and bicarbonate ions in the aqueous solution contributes to a decrease of the fluoride sorption capacity of the bone char by 79 and 31 %, respectively. Regeneration of the F-loaded bone char using 0.5 M NaOH solution leads to a sorption capacity for fluoride of 3.1 mg/g in the second loading cycle. Fluoride breakthrough curve obtained in a fixed-bed column presents an asymmetrical S -shaped form, with a slow approach of C / C 0  → 1.0 due to pore diffusion phenomena. 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Batch equilibrium studies were performed for the bone chars prepared using different procedures. The highest sorption capacities for fluoride were obtained for the acid washed ( q  = 6.2 ± 0.5 mg/g) and Al-doped ( q  = 6.4 ± 0.3 mg/g) bone chars. Langmuir and Freundlich models fitted well the equilibrium sorption data. Fluoride removal rate in batch system is fast in the first 5 h, decreasing after this time until achieving equilibrium due to pore diffusion. The presence of carbonate and bicarbonate ions in the aqueous solution contributes to a decrease of the fluoride sorption capacity of the bone char by 79 and 31 %, respectively. Regeneration of the F-loaded bone char using 0.5 M NaOH solution leads to a sorption capacity for fluoride of 3.1 mg/g in the second loading cycle. Fluoride breakthrough curve obtained in a fixed-bed column presents an asymmetrical S -shaped form, with a slow approach of C / C 0  → 1.0 due to pore diffusion phenomena. Considering the guideline value for drinking water of 1.5 mg F − /L, as recommended by World Health Organization, the service cycle for fluoride removal was of 71.0 h ([F − ] feed  ∼ 9 mg/L; flow rate = 1 mL/min; m sorbent  = 12.6 g). A mass transfer model considering the pore diffusion was able to satisfactorily describe the experimental data obtained in batch and continuous systems.</abstract><cop>Berlin/Heidelberg</cop><pub>Springer Berlin Heidelberg</pub><pmid>27815851</pmid><doi>10.1007/s11356-016-7816-5</doi><tpages>17</tpages><oa>free_for_read</oa></addata></record>
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subjects Adsorption
Animals
Aquatic Pollution
Aqueous solutions
Atmospheric Protection/Air Quality Control/Air Pollution
Bicarbonates
Bone and Bones
Bone composition
Bone growth
Bones
Carbonates
Cattle
Diffusion
Diffusion rate
Drinking water
Earth and Environmental Science
Ecotoxicology
Environment
Environmental Chemistry
Environmental Health
Environmental science
Equilibrium
Female
Flow rates
Flow velocity
Fluorides
Functional groups
Hydrogen-Ion Concentration
Kinetics
Mass transfer
Mathematical models
Mechanical loading
Phosphates
Regeneration
Research Article
Sodium hydroxide
Solutions
Sorption
Waste Water Technology
Water Management
Water Pollution Control
Water Purification - methods
title Cow bones char as a green sorbent for fluorides removal from aqueous solutions: batch and fixed-bed studies
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