| Literature DB >> 31597350 |
Flavia Lega Braghiroli1, Gisele Amaral-Labat2, Alan Fernando Ney Boss3, Clément Lacoste4, Antonio Pizzi5.
Abstract
Tannins are one of the most natural, non-toxic, and highly reactive aromatic biomolecules classified as polyphenols. The reactive phenolic compounds present in their chemical structure can be an alternative precursor for the preparation of several polymeric materials for applications in distinct industries: adhesives and coatings, leather tanning, wood protection, wine manufacture, animal feed industries, and recently also in the production of new porous materials (i.e., foams and gels). Among these new polymeric materials synthesized with tannins, organic and carbon gels have shown remarkable textural and physicochemical properties. Thus, this review presents and discusses the available studies on organic and carbon gels produced from tannin feedstock and how their properties are related to the different operating conditions, hence causing their cross-linking reaction mechanisms. Moreover, the steps during tannin gels preparation, such as the gelation and curing processes (under normal or hydrothermal conditions), solvent extraction, and gel drying approaches (i.e., supercritical, subcritical, and freeze-drying) as well as the methods available for their carbonization (i.e., pyrolysis and activation) are presented and discussed. Findings from organic and carbon tannin gels features demonstrate that their physicochemical and textural properties can vary greatly depending on the synthesis parameters, drying conditions, and carbonization methods. Research is still ongoing on the improvement of tannin gels synthesis and properties, but the review evaluates the application of these highly porous materials in multidisciplinary areas of science and engineering, including thermal insulation, contaminant sorption in drinking water and wastewater, and electrochemistry. Finally, the substitution of phenolic materials (i.e., phenol and resorcinol) by tannin in the production of gels could be beneficial to both the bioeconomy and the environment due to its low-cost, bio-based, non-toxic, and non-carcinogenic characteristics.Entities:
Keywords: biopolymer; carbon gel; hydrothermal carbonization; low-cost; organic gel; polyphenolic molecules; pore structure; porous materials; sol-gel; tannin
Year: 2019 PMID: 31597350 PMCID: PMC6843342 DOI: 10.3390/biom9100587
Source DB: PubMed Journal: Biomolecules ISSN: 2218-273X
Figure 1Polyflavonoids and carbohydrates linkage.
Figure 2The four repeating flavonoid units in condensed tannins.
Figure 3Chemical structure of phlobaphenes.
Figure 4Ferric tannates [31].
Figure 5Tridimensional structure of a tetraflavonoid 4,8-linked.
Figure 6(a) Schematic representation of sol-gel process of tannin gels and their respective SEM images at pH 4 (b) and pH 6 (c). Adapted with permission from reference [61]. Copyright 2013 Elsevier.
Figure 7Reaction mechanisms of a condensed tannin monomer with formaldehyde resulting in: (a) methylene bridges and (b) methyne ether bridges.
Figure 8Reactive sites of flavonoid units.
Figure 9Suggested cross-linking reactions on tannin-soy-formaldehyde gel (a) and 13C-NMR spectra of organic gel at pH 6 (b) [54].
Figure 10Phase diagram of the solvent within the gel structure and the representation of the different drying methods with their respective porous materials, adapted with permission from reference [92].
Organic and carbon gels synthesized at normal conditions.
| Precursors | Conditions | Main Findings | Ref. |
|---|---|---|---|
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| Tannin + formaldehyde (TF) | Hydrogels prepared at 85 °C for 120 h; | Organic aerogels; SBET = 219–880 m2/g; Porosity = 40–97% | [ |
| Tannin + formaldehyde + Pluronic (TFP) | Hydrogels prepared at 85 °C for 120 h with Pluronic® F-127, using a mass ratio of T/P of 2; | Organic xerogels; SBET = | [ |
| Tannin + soy + | Hydrogels prepared at 85 °C for 120 h; Proportions of T/S resin of 30 and 70 wt.% (on a dry basis), respectively; | Organic aerogels; SBET = 384–478 m2/g; Porosity = 84–88% | [ |
| Tannin + lignin + formaldehyde (TLF) | Hydrogels prepared at 85 °C for 120 h; Mass ratio of T/L of 0.11–1 (on a dry basis); | Organic aerogels; SBET = 50–550 m2/g; Porosity = 72%–87% | [ |
| Tannin + resorcinol + formaldehyde + sodium dodecyl sulfate (TRFSDS) | Preparation in oven: Hydrogels prepared at 85 °C for 72 h (gelation) and 48 h (curing); | Organic xerogels; Porosity = 20–85% | [ |
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| Tannin microspheres (TM) | Microspheres prepared at 80 °C for 1 h stirred at 200–1200 rpm; | Carbon xerogels; SBET = 7–666 m2/g | [ |
| Tannin + formaldehyde (TF) | Hydrogels prepared at 85 °C for 120 h; | Carbon aerogels; SBET = 580–720 m2/g; Porosity = 75–99% | [ |
| Tannin + resorcinol + formaldehyde (TRF) | Hydrogels prepared at 50 °C for 10–160 min (depending on gelation time); | Carbon cryogels; SBET = 30–650 m2/g; Porosity = 32–80% | [ |
| Tannin + formaldehyde (TF) | Hydrogels prepared at 85 °C for 120 h; | Carbon cryogels; SBET = 399–1420 m2/g; Porosity = 94–96% | [ |
| Tannin + pluronic + formaldehyde (TPF) | Hydrogels prepared at 85 °C for 120 h; | Carbon xerogels; SBET =5–877 m2/g; Porosity = 46%–86% | [ |
| Tannin (T) (autocondensation) | Tannin was added to solutions of Na2SiO3 (35 wt.%); | Carbon aerogels; SBET NaOH = 451–709 m2/g; SBET HF= 542–783 m2/g; Porosity = 67%–82% | [ |
| Tannin + sodium dodecyl sulfate + formaldehyde (TSDSF) | Hydrogels prepared at 85 °C for 72 h; | Carbon xerogels; Porosity = 25%–78% | [ |
| Tannin + formaldehyde (TF) | Hydrogels prepared at 85 °C for 120 h; | Activated carbon xerogels (ACX); SBET = 50–1810 m2/g | [ |
Figure 11Tannin-formaldehyde gels prepared with surfactant (a) top view, and without (b) bottom view. Reprinted with permission from reference [98]. Copyright 2011 Elsevier.
Figure 12Gels prepared under hydrothermal conditions with aqueous tannin solution at low pH (a) (Reprinted with permission from reference [106]. Copyright 2015 Elsevier), with metal salts (b) [113], and with aqueous evaporated aminated tannin (c) [114].
Organic and carbon tannin gels synthesized under hydrothermal conditions.
| Precursors | Conditions | Main Findings | Ref. |
|---|---|---|---|
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| Evaporated aminated tannin (EAT) | Hydrothermal gel: Amination at room temperature followed by evaporation and HTC of the solid material in water at 180 °C for 24 h; | Xerogel: SBET = 32 m2/g | [ |
| Evaporated aminated tannin (EAT) | Hydrothermal gel: Amination at room temperature followed by evaporation and HTC of the solid material in water at 180–220 °C for 24 h; | Xerogel: SBET = 64−102 m2/g | [ |
| Evaporated aminated tannin (EAT) | Hydrothermal gel: Amination at room temperature followed by evaporation and HTC of the solid material at mass fractions of 11, 18 and 27% in water at 180 °C for 24 h. The final gels were first soaked in ethanol for 3 days, and then subcritically (air and 80 °C), supercritically (CO2), and freeze-dried; | Xerogel, aerogel and cryogel: SBET = 102−295 m2/g | [ |
| Tannin (T) | Hydrothermal gel: Tannin aqueous solution under HTC conditions at 180 °C for 24 h; pTSA (para-toluenosulfonic acid) was used to change the pH from 4.2 to 1; Subcritical drying in two steps: air and 80 °C; | Xerogel: SBET = 1.25 m2/g | [ |
| Evaporated aminated (pine) tannin (EAT) | Hydrothermal gel: Amination at room temperature followed by evaporation and HTC of the solid material in water at 180 °C for 24 h; | Xerogel: Compacted monoliths having homogeneous spherical particles typical of gels. | [ |
| Bayberry tannin and graphene oxide (GO) | Hydrothermal gel: A mixture of graphene oxide and tannin at different mass ratios (1:0–1.5); | Hydrothermal cryogel: SBET = 75 m2/g | [ |
Figure 13Tannin-formaldehyde carbon aerogels prepared under normal conditions at pH 3.3 (a) and pH 8.3 (b) (Reprinted with permission from reference [77] Copyright 2011 Elsevier); and hydrothermal carbon gels prepared with tannin solution at pH 2 (c) (Reprinted with permission from reference [106] Copyright 2015 Elsevier) and at non-modified pH (4.2) (d) [114].
Applications of organic and carbon gels made from tannin.
| Application | Type of Gel | Testing Conditions | Main Findings | References |
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| Thermal insulator | Aerogel | Thermal conductivity of soy-tannin-formaldehyde in a cylindrical shape was performed at room temperature | Tannin gel conductivity is higher than that of air (0.033 W/mK compared to 0.026 W/mK). The presence of narrow mesopores and fewer macropores would be required to improve their performance as thermal insulators. | [ |
| Thermal insulator | Aerogel | Thermal conductivity of tannin-formaldehyde in a cylindrical shape was performed at room temperature | Tannin gel conductivity is close to that of air (0.027 W/mK). Low thermal conductivity was reported for gels with low density and very narrow pores. | [ |
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| Metal Pb2+ | Tannin-gel | Synthetic effluent 1000 mg/L, batch tests; ratio metal: adsorbent 0.1 g: 100 mL; Equilibrium time 5 h, pH = 1−7, T = 20 °C | Tannin-gel behavior as ionic exchanger: two Na+ ions exchanged by one Pb2+ ion. Pb removal efficiency increased from 58 to 115 mg Pb/g with increased pH from 3 to 4.2, respectively. | [ |
| Metal Cr6+ | Tannin-gel | Synthetic effluent 1000 mg/L, batch tests; ratio metal: adsorbent 2.5 g:100 mL; Equilibrium time 30 min, pH = 0.85–5, T = 30 °C | Adsorption mechanism consists of four steps: 1) Esterification of chromate with tannin molecules; 2) Reduction of Cr6+ into Cr3+; 3) Formation of carboxyl groups by tannin oxidation; and 4) Ion exchange of Cr3+ with carboxyl and hydroxyl groups. | [ |
| Metal Cr6+ | Tannin-gel | Synthetic effluent 500–5000 mg/L, batch tests; ratio metal: adsorbent 0.2 g:100 mL; Equilibrium time 8 h, pH = 1–12, T = 25–45 °C | Cr adsorption reached the maximum value of 488 mg/g at pH 1 (25 °C). The mechanism of Cr adsorption is based on: 1) Cr(IV) adsorption by phenolic groups through chromate esterification with tannin-gel surface; 2) Cr(VI) reduction to Cr(III); 3) Carboxylate group formation due to tannin-gel oxidation; 4) Cr(III) retention on tannin-gel surface; and finally 5) Cr adsorption through hydroxyl and carboxyl groups. | [ |
| Metal Cu2+ | Tannin-gel | Synthetic effluent 10−150 mg/L, batch tests; ratio metal: adsorbent 0.1 g:100 mL; Equilibrium time 3 h, pH = 2−5, T = 25 °C | Adsorption mechanism is a result of ion exchange or complexation between Cu2+ ions and phenolic groups present on tannin-gel surface. Adsorption decreases at lower pH due to ion exchange equilibrium. Maximum adsorption capacity: 44 mgCu/g at pH 5. | [ |
| Metal Zn2+ | Tannin-gel | Synthetic effluent, batch tests; Equilibrium time 2 weeks, pH = 7, T = 20 °C | Tannin-gel made from lab-extracted Pine tannin presented the best performance for Zn removal. | [ |
| Metal Ni2+ | Tannin-gel | Synthetic and real effluent (synthetic and river water) 50−200 mg/L, batch tests; ratio metal: adsorbent 0.25−1 g: 100 mL; Equilibrium time 35 min, pH = 2–7, T = 23 °C | The adsorption of Ni ions took place in a homogeneous tannin gel surface (monolayer adsorption). | [ |
| Metal Sr2+ | Hydrothermal cryogel | Synthetic effluent 10−150 mg/L, batch tests; ratio metal: adsorbent 0.02 g:100 mL; Equilibrium time 10 h, pH = 9, T = 25 °C | Graphene oxide-tannin gel prepared under HTC conditions showed excellent adsorption performance for the removal of Sr2+ (68 mgSr/g). Surface chemical analysis showed that Sr2+ was largely dependent on oxygen functional groups, pH, salinity and ionic strength. | [ |
| Rare metal V | Tannin-gel | Synthetic effluent 0.2 mM, batch tests; ratio metal: adsorbent 0.02 g:100 mL; Equilibrium time 1 h, pH = 1–8, T = 30 °C | V was efficiently adsorbed from different solutions: VOCl2 and NH4VO3. Stable compounds were formed between VO2+ (acid character) and catechol and pyrogallol (alkali behavior). V adsorption from NH4VO3 was based on adsorption of H3VO4 (pH = 3.75) and reduction of VO2+ to VO3- at pH 6. | [ |
| Rare metal Au | Tannin-gel | Synthetic effluent 10 mg/L, batch tests; ratio metal: adsorbent 0.01 g:100 mL; pH = 2−3.8, T = 20 °C | Adsorption of Au took place through the reduction of trivalent Au ions into metallic Au as well as oxidation of hydroxyl groups present in tannin-gel to carbonyl groups. | [ |
| Rare metal Au | Tannin-gel | Synthetic effluent 0.1 mM, column tests; Flow bed at 150 and 300 mL/h; pH = 2–6 | 98.5% of Au from HAuCl4 was adsorbed at pH 6. The mechanism of Au adsorption was based on: 1) Ligand exchange: AuCl4- with hydroxylphenyl groups present in the tannin-gel; 2) Reduction of Au(III) to Au(0); and 3) Adsorption of Au(0). | [ |
| Rare metal Pd(II) | Tannin-gel | Synthetic effluent 10 mg/L, batch tests; ratio metal: adsorbent 0.04 g:100 mL; pH = 1.3−2.5, T = 25 °C | Adsorption of Pd(II) was based on the inner sphere redox reaction: Pd(II) ions were adsorbed as metallic Pd; hydroxyl groups were oxidized; and a ligand-substitute Pd(II) tannin inner sphere complex was formed. | [ |
| Rare metal Pd(II) | Aminated tannin-gel freeze-dried | Synthetic effluent 100 mg/L, batch tests; ratio metal: adsorbent 0.1 g:100 mL; Acidic medium, T = 25 °C | Adsorption of Pd(II) was due to metal ions complexation and/or electrostatic interaction. Also, acidic metal ions had high affinity towards amine basic groups. | [ |
| Rare metals Pd and Pt | Aminated tannin-gel freeze-dried | Synthetic effluent 0.001 M, batch tests, single and multiple metal solutions; ratio metal: adsorbent 0.1 g:100 mL; Equilibrium time 20 h, pH = 0–5, T = 25 °C | The adsorption of Pd and Pt on tannin-gel surface increased with increasing pH and temperature, and with decreasing chloride ion concentration. The amino groups presented in tannin-gel formed stable complex with metal ions but the adsorbability of Pd(II) was much higher than Pt(IV). Interesting that aminated tannin gel adsorbed mostly Pd(II) from mixed solutions even though it had good adsorbability for Pt(IV) from single metal solution | [ |
| Rare metals Au, Pd, Pt and Rh | Tannin-gel | Synthetic effluent 1 mmol/L, batch tests, single and multiple solutions; ratio metal: adsorbent 0.1 g:100 mL; pH = 1, T = 25 °C | The predominant species of each metal were adsorbed by controlling the pH (equal to 1) as well as the redox potential differences between metals and tannin-gel. Au was selectively adsorbed and reduced because its redox potential was higher than that of tannin-gel. However, the other precious metals had much lower redox potential than that of tannin-gel. | [ |
| Metals: Au(III), Pd(II), Pt(IV), Cu(II), Fe(III), Ni(II), Zn(II) | Tannin-gel | Synthetic and real effluent, batch and column tests, single and multiple metal solutions; ratio metal: adsorbent 0.1–2 g:100 mL; Flow bed at 5 mL/h; Equilibrium time 12 h, acidic pH, T = 30 °C | Rare metals were efficiently adsorbed through both batch and column tests. Tannin-gel selectively adsorbed Au(III), Pd(II) and Pt(IV) over other metals: Cu(II), Fe(III), Ni(II) and Zn(II). The mechanism of adsorption of precious metals was the combination of ion exchange, electrostatic interaction and coordination with thiocarbonyl group. Au(III) was reduced to elemental Au through abundant polyphenolic groups on tannin molecule. Tannin-gel was regenerated under acid solution up to five times. | [ |
| Boron (B) | Aminated tannin-gel freeze-dried | Synthetic effluent 200 mg/L, batch tests; ratio contaminant: adsorbent 0.5 g:100 mL; Equilibrium time 20 h, pH = 8.8, T = 30 °C | Aminated and non-aminated gels efficiently adsorbed B at pH > 7. The adsorption of B took place through the chelate formation of tetrahydroxyborate ion and the hydroxyl and amino groups presented in tannin-gels. The adsorption capacity of the aminated cryogel was higher than that of non-aminated one due to the stable bonds between boron and nitrogen from amino groups. | [ |
| Phosphate (P) | Tannin-gel freeze-dried | Synthetic effluent 100 mg/L, batch tests; ratio contaminant: adsorbent 0.5 g:100 mL; pH = 2−12, T = 25 °C | The gel impregnated with iron and oxidized with nitric acid showed adsorption selectivity for phosphate. The adsorption process was independent of the pH (from 3 to 12). | [ |
| Organic MB | Tannin-gel | Synthetic effluent, batch tests; Equilibrium time 2 weeks, pH = 7, T = 20 °C | Tannin-gel made from lab-extracted Pine tannin presented the best performance for MB removal. | [ |
| Organic MB | Tannin-gel | Synthetic effluent 1000 mg/L, batch tests; Equilibrium time 15 days; pH = 4−10, T = 20 °C | Adsorption of MB was improved by increasing pH, probably because the dye appeared with a higher cationic degree and thus, it enhanced electrostatic interactions. | [ |
| Organic BR | Tannin-gel | Synthetic effluent 40 mg/L, batch tests; ratio contaminant: adsorbent 0.04 g:100 mL; Equilibrium time 1.5 h, pH = 2–8, T = 28 °C | Good adsorption of BR due to the presence of functional groups on tannin-gel structure: phenolic, carboxylic, alcoholic, ether and aromatic rings. Maximum adsorption capacity: 45 mgBR/g | [ |
| Organic CTAB | Tannin-gel | Synthetic effluent, batch tests; Equilibrium time 2 weeks, pH = 7, T = 20 °C | Tannin-gel made from lab-extracted Pine tannin presented the best performance for CTAB removal. | [ |
| Benzene and toluene | Tannin-gel | Synthetic effluents 1% sol., batch tests; Equilibrium time 1 h; ratio contaminant: adsorbent 0.1 g:100 mL; pH = 2–8.6, T = 60 °C | The removal of toluene was more effective than benzene probably because of the interactions between the methyl groups on toluene and the OH groups on tannin gel. Results show up to 99% removal of toluene and benzene after 30 min batch tests. | [ |
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| Thermal insulator | Carbon xerogel | Thermal conductivity of tannin-formaldehyde-surfactant in a cylindrical shape was performed at room temperature | Carbon tannin gel conductivity is higher than that of air (0.039 W/mK compared to 0.026 W/mK). The presence of narrow mesopores would be required to improve its performance as thermal insulator. | [ |
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| Supercapacitor | Carbon cryogel | Supercapacitor device based on a three-electrode cell configuration with an aqueous acid electrolyte (4 M H2SO4) | Carbon cryogels prepared at pH higher than 6 had low density and high surface areas (up to 1200 m2/g). Thus, such materials as electrodes for supercapacitor reached capacitances as high as 100 F/g (scan rate 2 mV/s). In addition to mesopores, ultra- and supermicropores played an important role on their performance as electrodes for supercapacitor. | [ |
| Supercapacitor | Hydrothermal carbon aero-, cryo- and xerogel | Supercapacitor device based on a three-electrode cell configuration with an aqueous acid electrolyte (4 M H2SO4) | Carbon aerogel, cryogel, and xerogel prepared from HTC of evaporated aminated tannin (MFTS of 27 wt.%) reached surfaces areas of 860, 754, and 585 m2/g and specific capacitances of 362, 387, and 330 F/g (scan rate 2 mV/s), respectively. The presence of nitrogen (2−3 wt.%) and oxygen (17−18 wt.%) functional groups played an important role on their performance for electrical energy storage, especially through pseudo-capacitance. However, mesostructuration within 3−13 nm should be created to improve the capacitance reduction at a higher scan rate. | [ |
| Supercapacitor | Hydrothermal carbon xerogel | Supercapacitor device based on a three-electrode cell configuration with an aqueous acid electrolyte (1 M H2SO4) | Hydrothermal carbon xerogel made from evaporated aminated Pine tannin reached a surface area and a specific capacitance of 485 m2/g and 253 F/g (scan rate 0.5 mV/s), respectively. The material presented high concentration of nitrogen and oxygen functional groups (6 mmol/g) that played an important role on their performance as electrodes for a supercapacitor. | [ |
MB: Methylene blue; BR: Brilliant red; CTAB: Cetyltrimethylammonium bromide.