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Proceeding Paper

Preparation of Ceramic Granules Enriched with Silicon Extracted from Reeds †

by
Mălina Deșliu-Avram
1,
Luiza Capră
1,
Ioana Tudor
1,
Carmen Lupu
1,
Diana Constantinescu-Aruxandei
1,
Orsolya Csilla Raduly
2,3,
Mariana Pătrașcu
4 and
Florin Oancea
1,3,*
1
Bioresources and Analysis Departments, National Institute for Research & Development in Chemistry and Petrochemistry—ICECHIM, Splaiul Independenței No. 202, Sector 6, 060021 Bucharest, Romania
2
Faculty of Biotechnologies, University of Agronomic Sciences and Veterinary Medicine of Bucharest, Bd. Marasti Nr. 59, Sector 1, 011464 Bucharest, Romania
3
Chemi Ceramic F Srl, Str. Ciucului Street nr. 163, 520036 Sfântu Gheorghe, Romania
4
Research & Development Department, Primosal Srl, Str. Dreptății Nr. 6, 060886 Bucharest, Romania
*
Author to whom correspondence should be addressed.
Presented at the Exploratory Workshop “Innovative Cross-Sectoral Technologies”, Vth Edition, Bucharest, Romania, 22–23 May 2023, Secvent Project Meeting.
Chem. Proc. 2023, 13(1), 31; https://doi.org/10.3390/chemproc2023013031
Published: 20 December 2023

Abstract

:
This article presents the microwave-assisted extraction of biosilica from common reed (Phragmites australis) biomass and the utilization of the resulting aqueous extract to enrich porous ceramic granules based on diatomaceous earth and bentonite from white wine cleaning. The enriched porous ceramic granule generated a solution of soluble silicon that was +23.4 ± 2.2 more concentrated than the porous ceramic granules not enriched with reed extract. The water reactivity of Si-O-Si groups is higher in the polysilicic acid formed via the polycondensation of silicic acid extracted from reed, compared to the Si-O-Si group from diatomaceous earth or bentonite.

1. Introduction

The common reed (Phragmites australis) influences wetland biodiversity and wetland ecosystem resilience [1,2]. Harvesting reed biomass and its utilization in the construction, paper, and energy industries is one of the leading solutions for wetland ecosystem management that includes reeds control [3].
The main issue with the industrial processing of reed biomass is related to its high biosilica content, which increases the risk of silica scale [4]. The pretreatment of reed biomass for biosilica extraction reduces the silica scale risk and represents a solution to close the loop of the biosilica cycle [5].
One gap in reed biosilica loop closure is the appropriate soil application formulation of the extracted soluble silicon [5]. The solution investigated in this article is the embedment of the silicon species resulting from the concentrated aqueous reed extract in porous ceramic granules that include diatomaceous earth and bentonite from the winemaking industry.
Porous ceramic granules are inorganic soil conditioners that improve soil structure, increase soil resistance to compaction, and promote healthy root systems [6,7]. Our group previously developed ceramic granules, wherein diatomaceous earth was included as a source of soluble silicon species for an enhanced plant biostimulant effect [8]. This solution was further developed using bentonite from the wine clarification process [9] as a sacrificial pore-generating agent in ceramic granules intended for soil treatment. The utilization of spent bentonite recycles a byproduct of the winemaking industry. Spent bentonite gives superior properties to ceramic granules as a soil conditioner due to the addition of bentonite, with a proven ability to modulate the bioavailability of water and mineral nutrients in soil [10,11].
The embedment of the concentrated reed extract with polycondensate silicon species in ceramic porous granules is intended to enrich these granules with chemical structures that slow-release soluble silicon species. In a water environment, silicic acid at a concentration higher than 1 mM starts to polycondensate, generating polysilicic acid, SiOnH2O. This polycondensation reaction is reversible; the polysilicic acid structures hydrolyze in an aqueous solution wherein the silicic acid concentration is lower than 1 mM, releasing orthosilicic acid, H4SiO4. In a cultivated soil environment, the plant roots uptake silicic acid in concentrations between 0.1 and 0.6 mM [12], maintaining a constant slow release of soluble species into the soil solution.
This paper presents the microwave extraction of silicon species from reeds and the process of enriching the ceramic granules with the concentrated aqueous reeds extract.

2. Materials and Methods

2.1. Materials

Two reed (Phragmites australis) samples (S1 and S2) were taken from the Danube Delta, from a location near Mila 23 village, at 45°13′23′23″ N, 29°14′44′44″ E, 2 m altitude, in February 2023. For manufacturing ceramic granules, clay, quartz sand, silica sol, diatomaceous earth, and bentonite from white wine clarification were used. The clay was extracted from the Bodoc site and contains 69.97% SiO2, 15.41% Al2O3, 4.88% Fe2O3 [13]. The quartz sand contains more than 97% SiO2. The used diatomaceous earth (DE) was from Sibiciu de Sus quarry (Industriile de Diatomit, Pătârlagele, Buzău, Romania), and was formed by frustules of freshwater diatoms from the Aulacoseira (66%) and Actinocyclus genera [14]. The bentonite was from clarification of Muscat Ottonel white wine (Miniș, Romania). The montmorillonite content of the used bentonite was 72%.
The reagents used to determine the elemental composition of aqueous reed extract quantitatively were of analytical purity. Standard solutions, Certipur, with a concentration of 1000 mg/L, from Merck (Merck Group, Darmstadt, Germany) were used. Ultrapure water produced by Milli-Q, Integral Sistem (Millipore, Merck Group, Darmstadt) with a resistivity of 18.2 MΩ/cm was used to prepare the working solutions and samples. The purge gas for ICP-OES (inductively coupled plasma–optical emission spectrometry) was Argon 5.0 of 99.999% purity (Siad, Călărași, Romania).

2.2. Microwave-Assisted Extraction of Silicon Species from Reeds

The microwave-assisted extraction of reed biomass is illustrated in Figure 1.
The dried reed biomass was shredded with a UD2500 electric shredder (Makita, Anjo, Japan), followed by grinding with a laboratory mill with two knives (M20, IKA, Staufen, Germany), to a maximum size of 0.5 cm [15].
The microwave-assisted extraction was carried out in two main variants: heating on a microwave oven, after heating and mixing reed biomass with water in a hot stirring plate, and in a microwave extraction system.
In the first variant, two approaches were used. In the first approach, a solid/liquid (S/L) mixture was produced in a ratio of 1:30, respectively, 5 g processed reed to 150 mL ultrapure water Milli-Q, in 0.5 L Erlenmeyer flasks with a wide neck and screw cap, made from polypropylene (Corning®, Corning Inc., Corning, NY, USA). Extractions were performed in triplicate. The reed used had a moisture content of 4.36%. The mixture was heated on a magnetic hot plate, MR Hei-Tec (Heidolph, Schwabach, Germany), with a water bath at 50 °C for 2 h, and then the mixture was placed in a microwave oven, AT325 (Whirlpool, Benton Harbor, MI, USA), for 5 min. The microwave extraction was performed in stages. After every 30 s of heating, extraction was stopped for 1 min.
After microwave-assisted extraction, the mixture was centrifuged in a Universal 320R centrifuge (Hettich, Tuttlingen, Germany) for 15 min, 7200× g, temperature 25 °C, and the supernatant was filtered through filter paper, Filtrak no. 390. The volume was measured, and the total Si content of samples S1.1 and S2.1 was analyzed via ICP-OES. The sediment was recovered, dried in a laboratory oven, UN 200 (Memmert, Schwabach, Germany), at 105 °C for 4 h, and its dried weight was measured using a precision balance (XPR204S, Metler-Toledo, Columbus, OH, USA).
In the second approach, microwave-assisted extraction was performed with fresh pure water for 10 min. After 2 h on the magnetic plate, the samples were centrifuged, and the supernatant was filtered and analyzed for the total silicon content (leading to S1.2 and S2.2). Over the wet sediment, 100 mL of ultrapure water Milli-Q was added, and the wet reed biomass was further extracted for 10 min in the microwave oven. The final mixture was centrifuged, the supernatant was filtered and analyzed for total Si content (resulting S1.3 and S2.3), and the sediment was recovered, dried, and weighed.
The same S/L ratio was used in the second variant, but with larger quantities. A 20 g ground reed biomass sample was mixed with 600 mL ultrapure water Milli-Q. The extraction was conducted directly in a microwave system (Minilabotron 2000, model M20K230, Sairem, Décines-Charpieu, France) equipped with a round-bottomed glass flask, magnetic stirring, and ascending refrigerant connected to water. In this variant, a blank sample was performed only with ultrapure water Milli-Q, under the same conditions, to quantify and further deduct the silicon extracted from the glass flask. Before the microwave extraction, the reed sample was stirred for wetting at room temperature, at 900 rpm, on a magnetic stirrer (Arex 6, Velp Scientifica, Usmate Velate, Italy) for 5 min. Then, the mixture was placed in the microwave system and heated until it reached the boiling temperature of water (~95 °C). The sample was extracted at boiling temperature for 5 min, under reflux at an applied power (PI) of 200 W. After the microwave-assisted extraction, the sample was processed as in the first variant: centrifugation, supernatant filtration, sediment recovery, drying, and weighing. In the supernatant S2.4, besides the content of Si, other elements were determined: Ca, Mg, K, Na, P, Cu, Cd, Pb, Cr, and Ni.

2.3. Element Analysis Using ICP-OES

The content of Si Ca, Mg, K, Na, P, Cu, Cd, Pb, Cr, and Ni from the aqueous extract was determined using the Optima 2100 DV ICP-OES System (Perkin Elmer, Waltham, MA, USA), according to SR EN ISO 11885:2009 standard [16], with dual-view optical system—axial and radial plasma view in a single work sequence, which works with an independent transistorized radio frequency generator with a frequency of 40 MHz. The nebulization system used has a PEEK Mira Mist® nebulizer coupled with the Baffled Cyclonic spray chamber. The spectrometer comprises an optical module with an Echelle monochromator with a two-dimensional CCD (charged coupled device) detector, the spectral range being 165–800 nm [17]. The samples were mineralized according to the already-described protocol [18], and the sample concentration was calculated based on calibration curves.

2.4. Enrichment of Ceramic Granules with Silicon

Wet ceramic granules with diatomite and bentonite were fabricated at room temperature via pan granulation up to the desired size of approximately 10 mm, according to the already described method [13]. The granules were sintered at 960 °C in a laboratory furnace (CWF, Carbolite-Gero, Verder Scientific, Haan, Germany). The porous granules have a specific surface of 2.145 m2/g. The S2.4 extract was concentrated 10 times in a rotary evaporator (Rotavapor® R-300, Büchi, Flawil, Switzerland). Fifty grams of porous granules were mixed with 100 mL of concentrated extracts, dried at room temperature for 24 h, and then at 104 ± 2 °C for 4 h in a vacuum oven (VD, Binder, Tuttlingen, Germany). To demonstrate the enrichment with slow-releasing silicon species, 10 g of ceramic granules, enriched and non-enriched with reed extract, were mixed with 500 mL pure water MilliQ for 12 h in a magnetic stirrer (Arex 6, Velp Scientifica, Usmate Velate). The soluble silicon species were determined with ammonium molybdate reagent [19].

2.5. FT-IR Spectroscopy

The diatomaceous earth, bentonite, and freeze-dried reed extract (that contains amorphous silica) were subjected to attenuated total reflection (ATR)—Fourier transform infrared (FTIR) spectroscopy. The equipment used comprised an IRTracer 100 spectrophotometer (Shimadzu, Kyoto, Japan). The vibrational spectra were analyzed in the wavenumber range between 4000 and 400 cm−1, with a resolution of 4 cm−1, and 45 scans per sample.

3. Results and Discussion

The total silicon content in different samples of microwave-assisted extracted reed biomass is presented in Table 1.
The energy transferred to the system is essential for the solubilization of the biosilica from reed biomass. The application of 700 W power for 10 min determined an increase in the concentration of the extracted total silicon compared to the application for 5 min of the 700 W power.
The most efficient microwave-assisted extraction is with the Minilabotron 2000 microwave system. This system, designed for the targeted application of microwaves, extracted significantly more silicon from reed biomass when 200 W was applied for 5 min than the microwave oven at a power of 750 W for 5 or 10 min.
In the reed biomass, biosilica is present in two forms, phytoliths, i.e., opal silica bodies, SiOnH2O, formed via the polycondensation of the silicic acid accumulated between cytoplasmatic membranes and cell walls [20,21] and silicic acid complexed in the lignocellulosic matrix [22]. The energy is needed to extract the silicic acid from its hemicellulose complex and accelerate silicic acid solubilization from opal silica. The Minilabotron 2000 microwave system targets more efficient microwave energy and produces more efficient vibration at the molecular level—and further, this molecular vibration is transformed into heat. In a microwave oven, the energy is not focused and dissipates faster as heat.
The concentrations of the elements for the reed sample S2.4 analyzed are presented in Table 2, at the corresponding wavelengths (λ) of determination.
Table 2 shows that the reed sample is rich in Si and K, followed by Na, Ca, Mg, P, and a small amount of the heavy metals Pb, Cu, Cd, Ni, and Cr, under the threshold limit for fertilizing products recovered from biomass [23].
The porous ceramic granules enriched with reed extract generated a solution of soluble silicon that was +23.4 ± 2.2 more concentrated than those not enriched with reed extract. The water reactivity of Si-O-Si groups is higher on the polysilicic acid formed via the polycondensation of silicic acid extracted from reed, compared to the Si-O-Si groups from diatomaceous earth or bentonite.
The FTIR analysis is relevant regarding Si-O-Si groups from diatomaceous earth, bentonite, and amorphous silica resulting from extracted biomass reed. Figure 2 shows the characteristic vibrational spectra of these materials.
The stretching vibration spectra corresponding to diatomaceous earth are represented by a high silica content (over 80%). The silanol Si-OH groups are found at 3700 cm−1 (they were formed as a result of water adsorption in the diatomite structure), the peak at 1568 cm−1 corresponds to some carbonate groups (in small amounts, in the form of traces [24], and the peak at 1408 cm−1 belongs to some OH groups, suggesting the presence of residual water in the system. The peak at 1045 cm−1 describes the asymmetric stretching vibrations of the siloxane (Si-O-Si), and in the area 795-455 cm−1 are the symmetric bands of the silicates represented by the groups Si-O-Si, Si-O-, and O-Si-O. According to Figure 2a, in comparison to amorphous silica Figure 2b, it is found that in the structure of the diatomite, there is an amorphous structure (given by the presence of the peaks at 1045 cm−1; the other peaks at 795 cm−1, 617 cm−1, and 455 cm−1 show some delocalization and transformations), but also the presence of crystalline structures represented by calcite (the peak at 1568 cm−1), and quartz with a low content of cristobalite (through the symmetrical bands at 795 cm−1 and 455 cm−1, where the peaks become sharper compared to the amorphous form) [25].
Bentonite exhibits a dioctahedral structure of smectite (either calcium or sodium montmorillonite or both) [26] with 2:1 stacked layers (TOT) with two tetrahedral (T) starts of electrostatically cross-linked silica (SiO4) with a central layer of aluminum oxide (Al2O3) or iron (Fe2O3) arranged octahedrally (O) [27]. The layers are held together by van der Waals forces that allow the structure to rearrange. The tetrahedral structure given by the SiO4 groups is highlighted by the peaks at 1031 cm−1, 789 cm−1, and 463 cm−1 [28]. The peak at 1645 cm−1 indicates the presence of deformation vibrations of adsorbed water in the system [29], and the peak at 1528 cm−1 shows the stretching vibrations of the hydroxyl groups. The symmetrical stretching bands of the peak at 789 cm−1 attest to the presence of the Fe-OH-Mg bond, describing the Mg2+-enriched structure with low Fe3+ content [30]. In the area below 1000 cm−1, symmetrical stretching bands that correspond to Si-O-, Si-O-Si bonds can also be found.

4. Conclusions

The silicon is efficiently extracted with a microwave applied in the Minilabotron 2000 system, due to the targeted application of the energy. The extracted liquid with high silicon and potassium content was used to enrich porous ceramic granules. The enriched ceramic granules, with a higher releasing rate of soluble silicon species, are good candidates for a multifunctional product, acting as both a soil conditioner and plant biostimulant.

Author Contributions

Conceptualization, F.O. and D.C.-A.; methodology, M.D.-A. and O.C.R.; software, F.O.; validation, C.L., L.C. and D.C.-A.; formal analysis, F.O.; investigation, M.D.-A., I.T., O.C.R. and M.P.; resources, F.O.; data curation, D.C.-A.; writing—original draft preparation, M.D.-A.; writing—review and editing, F.O. and D.C.-A.; visualization, I.T. and D.C.-A.; supervision, F.O.; project administration, C.L. and M.D.-A.; funding acquisition, F.O. All authors have read and agreed to the published version of the manuscript.

Funding

The research leading to these results has received funding from European Regional Development Fund (ERDF), the Competitiveness Operational Program (POC), Axis 1, project POC-A1-A1.2.3-G-2015-P_40_352, My_SMIS 105684, “Sequential processes of closing the side streams from bioeconomy and innovative (bio)products resulting from it—SECVENT”, subsidiary projects 1818/2020—AgriCem and 617/2022 DiaCer.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

All data generated or analyzed during this study are included in this published article.

Conflicts of Interest

O.C.R. was employed by Chemi Ceramic F and M.P. is employed by Primosal. The other authors declare no conflicts of interest. The above mentioned companies and the funder had no role in the design of the study; in the collection, analyses, or interpretation of data; in the writing of the manuscript; or in the decision to publish the results.

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Figure 1. The process for microwave-assisted extraction of silicon species from reed biomass.
Figure 1. The process for microwave-assisted extraction of silicon species from reed biomass.
Chemproc 13 00031 g001
Figure 2. ATR-FT-IR spectra for: (a) diatomaceous earth (diatomite) and bentonite, and (b) amorphous silica resulting from extracted reed biomass.
Figure 2. ATR-FT-IR spectra for: (a) diatomaceous earth (diatomite) and bentonite, and (b) amorphous silica resulting from extracted reed biomass.
Chemproc 13 00031 g002
Table 1. Total silicon content in different samples of microwave-assisted extracted reed biomass.
Table 1. Total silicon content in different samples of microwave-assisted extracted reed biomass.
SampleTotal Si,
% (w/w)
Sediment
(% of Initial Sample)
S1.10.07386.02
S2.10.09087.53
S1.20.038-
S2.20.025-
S1.30.17788.64
S2.30.17488.82
S2.40.20592.44
Table 2. The concentrations of the elements for the reed sample.
Table 2. The concentrations of the elements for the reed sample.
AnalyteConcentrationUnit
Si (λ = 251.611 nm)0.135% (w/w)
Ca (λ = 317.933 nm)418mg/Kg
Mg (λ = 285.213 nm)297mg/Kg
P (λ = 213.617 nm)159mg/Kg
Na (λ = 589.592 nm)872mg/kg
K (λ = 766.490 nm)0.131% (w/w)
Cu (λ = 327.393 nm)<2.4 *mg/Kg
Cd (λ = 214.440 nm)<1.8 *mg/Kg
Pb (λ = 220.353 nm)<2.6 *mg/Kg
Cr (λ = 267.716 nm)<0.9 *mg/Kg
Ni (λ = 231.604 nm)<1.3 *mg/Kg
* marked values represent the quantification limits of the determination methods.
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Deșliu-Avram, M.; Capră, L.; Tudor, I.; Lupu, C.; Constantinescu-Aruxandei, D.; Raduly, O.C.; Pătrașcu, M.; Oancea, F. Preparation of Ceramic Granules Enriched with Silicon Extracted from Reeds. Chem. Proc. 2023, 13, 31. https://doi.org/10.3390/chemproc2023013031

AMA Style

Deșliu-Avram M, Capră L, Tudor I, Lupu C, Constantinescu-Aruxandei D, Raduly OC, Pătrașcu M, Oancea F. Preparation of Ceramic Granules Enriched with Silicon Extracted from Reeds. Chemistry Proceedings. 2023; 13(1):31. https://doi.org/10.3390/chemproc2023013031

Chicago/Turabian Style

Deșliu-Avram, Mălina, Luiza Capră, Ioana Tudor, Carmen Lupu, Diana Constantinescu-Aruxandei, Orsolya Csilla Raduly, Mariana Pătrașcu, and Florin Oancea. 2023. "Preparation of Ceramic Granules Enriched with Silicon Extracted from Reeds" Chemistry Proceedings 13, no. 1: 31. https://doi.org/10.3390/chemproc2023013031

APA Style

Deșliu-Avram, M., Capră, L., Tudor, I., Lupu, C., Constantinescu-Aruxandei, D., Raduly, O. C., Pătrașcu, M., & Oancea, F. (2023). Preparation of Ceramic Granules Enriched with Silicon Extracted from Reeds. Chemistry Proceedings, 13(1), 31. https://doi.org/10.3390/chemproc2023013031

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