Biogenic Nanosilica Synthesis Employing Agro-Waste Rice Straw and Its Application Study in Photocatalytic Degradation of Cationic Dye

Abstract

The current study aims towards a holistic utilization of agro-waste rice straw (RS) to synthesize nanosilica (SiNPs) employing the sol–gel method. The effect of ashing temperature was evaluated for the synthesis process. X-ray diffraction demonstrated a broad spectrum at 21.22° for SiNPs obtained using RSA-600, signifying its amorphous nature, whereas crystalline SiNPs were synthesized using RSA-900. The EDX and FTIR spectra confirmed the significant peaks of Si and O for amorphous SiNPs, confirming their purity over crystalline SiNPs. FE-SEM and TEM micrographs indicated the spheroid morphology of the SiNPs with an average size of 27.47 nm (amorphous SiNPs) and 52.79 nm (crystalline SiNPs). Amorphous SiNPs possessed a high surface area of 226.11 m²/g over crystalline SiNPs (84.45 m²/g). The results obtained attest that the amorphous SiNPs possessed better attributes than crystalline SiNPs, omitting the need to incorporate high temperature. Photocatalytic degradation of methylene blue using SiNPs reflected that 66.26% of the dye was degraded in the first 10 min. The degradation study showed first-order kinetics with a half-life of 6.79 min. The cost-effective and environmentally friendly process offers a sustainable route to meet the increasing demand for SiNPs in industrial sectors. The study proposes a sustainable solution to stubble burning, intending towards zero waste generation, bioeconomy, and achieving the Sustainable Development Goals (SDGs), namely SDG 13(Climate Action), SDG 3(Good health and well-being), SDG 7(use of crop residues in industrial sectors) and SDG 8 (employment generation).

1. Introduction

Rice straw (RS), lignocellulosic biomass, is a very common agro-waste generated in the agriculture system after the post-harvesting of rice. Incorporating the crop and harvesting method, approximately 40–60% of residual biomass comprises RS [1,2]. RS is a stiff, voluminous lignocellulosic biomass with significant silica (SiO₂) deposits, for which the level of biogenic silica can reach up to 82% on a dry weight basis. The complex structure limits the usability of RS. Being a quick, easy and cheap process, most farmers opt for open field-burning as the most preferred approach to dispose of RS in agricultural fields [3,4]. The burning of farm waste causes the ghastly pollution of soil and water at the regional scale. This practice also adversely reduces the nutrient composition in the soil. The elemental carbon, nitrogen and sulphur become completely burnt and subsequently emit hazardous gases such as methane, nitrogen oxide and ammonia, causing austere atmospheric pollution. These gases also contribute and further add up to the existing ozone pollution. Burning releases fine particles which are known to aggravate chronic heart and lung diseases [3].

Rice plants accumulate Si by polymerizing water-soluble silicic acid (H₄SiO₄) absorbed from the soil into insoluble polysilicic acids, precipitated as amorphous silica and deposited on the plant cell’s exterior [5,6]. Si is deposited in plants primarily as phytoliths, which consist of amorphous hydrated silica. These beneficial attributes and the rich Si content of RS make it a suitable alternate source of biogenic nano-silica [7]. The Si can be extracted from RS by ashing at a temperature beyond 400 °C. However, temperature above 700 °C leads to the production of crystalline Si such as cristobalite and tridymite, with limited applications, possessing higher risks of silicosis [8,9,10].

In recent years, many efforts have been made to synthesize silica nanoparticles (SiNPs) from various preparatory materials, precisely chemical and natural sources. Different approaches such as the sol−gel process, chemical precipitation method, microemulsion processing, plasma synthesis, chemical vapor deposition, combustion in a diffusion flame and hydrothermal treatment have been employed for preparing Si-NPs [11,12]. Among these, the sol−gel process, also known as the “Stöber method” is a relatively modest and low-cost process [13,14]. It is worth highlighting that the chemical route is not only expensive, but it also adds to the list of pollutants, therefore, adapting a green route is the need of the hour for a healthy and safe environment [15].

The scientific community has successfully utilized the potential of nanotechnology to develop different products and materials at the nanoscale for societal welfare [12,16]. Silica is an important inorganic material with a panoramic range of applications in the textile industry, automobile industry, biology, medicine, adsorbents, drug delivery system, etc. [11,12,17]; additionally, it also holds an advantage over conventional precursors owing to its abundancy as well as being a cheap substrate [18].

SiNPs holds potential application in various sectors due to its high surface area and reactivity in broad areas [12,13,19,20]. These versatile properties enhance their potentials for developing biosensors and biomarkers, holding application in the detection of platelet-derived microparticles and the identification of leukemia cells [21]. The combination of SiNPs with super absorbent polymers helps in assuaging the plastic shrinkage. Additionally, the unique ability of SiNPs to exhibit the nucleation effect and pozzolanic activity leads to a decrease in the setting time and the mitigation of calcium leaching losses for cement-based materials [22,23]. The suitability of SiNPs as fillers in nanosilica composites has also been investigated by Salimian et al. [24]. The unique ability of SiNPs also tends to enhance its catalytic and photocatalytic applicability for removing an organophosphate pesticide, elimination of heavy metals from wastewater, the treatment of textile effluents and dye decolorization [23,25].

Of the various pollutants reported, methylene blue is a prominent blue cationic thiazine dye used widely in textile, paper and wood industries. It is documented that intense exposure to this dye leads to release of aromatic amines with severe environmental and health hazards. In previous years, chemical-based products have been designed to degrade toxic pollutants effectively; yet again, the persistent and non-degradable nature with its known tendency to bioaccumulate serves well as another potential environmental health hazard, demanding an adequate replacement [26,27].

In this regard, nanomaterials have emerged as an influential factor in removing organic pollutants due to their excellent high surface area and adsorption capacity. Exploring the potential of naturally synthesized nanomaterials holds potential utility. With reference to the proposed methods, although silica is inert for many reactions, it shows noticeable catalytic activities under ultraviolet irradiation below ~390 nm, e.g., photo-oxidation of CO, photo-metathesis of propene, photo-epoxidation of propene and silica-based photocatalysts such as silica-alumina, silica-alumina-titania and gold-coated SiO₂ with practical photocatalytic activities possessing a significant utility in photodegradation of toxic products [27,28,29]. The utilization of agro-waste-derived SiNPs in the degradation of cationic dye serves as an excellent example of two birds with one stone, on one end promoting a natural route towards the treatment of the toxic effluents while on the other proposing an excellent alternative towards the minimization of chemical-based routes for the treatment of organic pollutants.

A dearth of literature highlights the difference observed in the characterization of SiNPs when RS ashing is performed at 900 °C vs. the ashing temperature of 550 to 600 °C. To this end, a comparative analysis of amorphous and crystalline SiNPs synthesized using the sol–gel method was conducted in the current study to empirically attest the amorphous SiNPs as a preferential choice over crystalline SiNPs. The optimal SiNPS were further explored for a cost-effective route for the removal of the toxic pollutant methylene blue. The study offers insights to researchers and stakeholders towards a sustainable route for the synthesis of SiNPs and its application in the degradation of the toxic cationic dye methylene blue. The increase in the utility of silica-rich RS can serve as an integral factor in avoidance of stubble burning and exploring its utility will provide new ventures towards a suitable replacement to chemical route adopted to eliminate the toxic dyes in industries, thus playing an integral role towards bioeconomy as well as to the safe and healthy environment. The study overall is an attempt to meet the Sustainable Development Goals (SDGs). An alternative to stubble burning will assist in targeting SDG 13 (Climate Action), SDG 3 (Good health and well-being), SDG 7 (Use of crop residues in industrial sectors) and SDG 8 (Employment generation), highlight the aim of the study undertaken [30].

2. Materials and Methods

2.1. Collection of Raw Material and Rice Straw Ash Preparation

RS was collected from the Khatauli village of Uttar Pradesh, India. Before any treatment, the piled agro-residue was washed thoroughly using distilled water and then dried at 105 °C. Dried RS was chopped into small pieces and pulverized in a supermass collider (Masuko Sangyo Co. Ltd., Kawaguchi, Japan). For uniform size powdered straw, the pulverized material was passed through a 20-mesh screen. The ground RS powder was re-washed to remove any dust particles and dried in a hot air oven at 60 °C. Finally, dried and cleaned straw powder was burned to ashes using a muffle furnace, maintaining the furnace temperature at 600 °C and 900 °C for 4 h leading to grey and white ash production, respectively [12]. The ashes obtained at two different temperatures are denoted hereafter as RSA-600 and RSA-900, used to synthesize SiNPs.

2.2. Nano Silica Extraction from Rice Straw Ash

A combined method for extracting nanosilica from RS was performed based on the methodology provided by Bahrami et al. [10] and Kalapathy et al. [31]. A detailed methodology followed is outlined in Figure 1.

2.3. Characterization of Rice Straw Ash and Nanosilica Powders

2.3.1. X-ray Diffraction (XRD)

The amorphous and crystalline nature of calcinated RSAs and synthesized SiNPs were determined using XRD X’Pert Pro (PANalytical The Netherlands). The samples were flattened in the sample container using a glass slide. Radical scans of scattering angle (2θ) vs. intensity scans were recorded from 5 to 100° with CuKα radiation of 1.54 Å.

2.3.2. Fourier Transform Infrared Spectroscopy (FTIR)

The functional bonds present in the RSA and SiNPs were studied using an FTIR spectrophotometer (Perkin-Elmer1600). The absorbance of the dried sample was measured in the spectral range of 4000–500 cm⁻¹ for 128 scans at a speed of 16 cm s⁻¹. The spectral obtained was compared with the commercial nanosilica based on a literature review [4].

2.3.3. Field Emission Scanning Electron Microscope-Energy Dispersive Spectroscopy (FE-SEM-EDX)

Microstructure and surface characteristics of the substrates (Raw RS, RSA, and SiNPs) were observed using FE-SEM-EDX (Field Emission Scanning Electron Microscope with Oxford-EDX system IE 250 X Max 80, The Netherlands). The dehydrated sample was mounted on the carbon tape. Gold sputtering was performed under vacuum 120 s with an acquisition time of 2 min, beam accelerating voltage of 10 kV at beam aperture (30 mm), with a working distance of 10 mm and probe current of 3 × 10⁻¹⁰ A. Mean EDX count rate was kept as 1600 ± 200 cps.

2.3.4. Transmission Electron Microscopy (TEM)

TEM analyses were performed by dissolving 5 mg of samples (RSA and SiNPs) in 50 mL of double distilled water and kept for 30 min ultrasonication. Next, 10 μL of the suspension (0.005% w/w) was mounted on carbon-coated copper grids. The shape and size of the samples prepared were characterized by TEM (JEOL JEM-1400) at an accelerating voltage of 100 kV. The diameter and size distribution of synthesized SiNPs was calculated using ImageJ software.

2.3.5. Surface Area and Porosity

A Brunauer–Emmett–Teller (BET) of the make (Micromeritics ASAP 2010, USA) was used to analyze the surface area of synthesized SiNPs at 77 K in N₂ atmosphere. The pore size distribution of the catalyst was calculated from the Barret–Joyner–Halenda (BJH) method using the adsorption data at relative pressure P/P₀ – 0.990.

2.3.6. Photocatalytic Degradation of Methylene Blue Dye

The photocatalytic effect of different concentrations of the optimum synthesized SiNPs (0.2–0.5 g/L) on methylene blue (100 ppm) at alkaline pH 11.0 was investigated following the protocols of Saleh and Dijaja [29] and Aly and Elhamid [26] with slight modifications. The photocatalytic experiment was conducted in a glass beaker equipped with continuous stirring under exposure to ultraviolet light (Philips 30 W, two tubes). Different suspensions were swirled in the dark for 30 min before irradiation to obtain a colloidal solution. The beakers were placed at a 15 cm distance from the light source. The samples were extracted every 2 h and centrifuged at 10,000 rpm for 5 min, and the study was conducted for 2 h. The absorbance of the solution was determined using a BioTek Epoch 2 microplate spectrophotometer at 630 nm (λmax), corresponding to the maximum absorption of methylene blue. The dye removal efficiency percentage was calculated as (A₀-At)/A₀ × 100, where A₀ and A_t are the initial and final dye concentrations at time t, respectively.

3. Results

3.1. X-ray Diffraction Analysis

The XRD analysis of RSA-600 depicted a broad hump between 20.52°–22.71°, indicating the material to be amorphous (Figure 2A), possessing the ability for adsorption; whereas RSA-900 indicated sharp peaks between 20°and 30° (Figure 2B), documented to decrease the available surface area, thus restricting the adsorption potential [8].

The synthesis process of SiNPs carried out using RSA-600 depicted a broad peak centered at 22°; the absence of any other peaks confirmed the SiNPs to be of amorphous nature (Figure 2C). SiNPs synthesized from RSA-900 depicted the presence of crystalline components between 20°–30° with a crystallinity index of 65%, calculated according to the methodology of Mendes et al. [32]. However, various other peaks signified the impurity of the synthesized product, as shown in Figure 2D. The results are in coherence with the findings of several other researchers, where the diffraction peaks at 2θ angles between 20° and 30° is documented to be the characteristic peak of silica [6,33].

3.2. EDX Analysis

The EDX profiling of RSA-600 showed Si and O’s presence and various other minor elements such as Mg, K, Na, Al, S, Fe and Ca, shown in Figure 3A. The profiling study of white RSA-900 also showed various elements along with Si and O, with a low K content, as shown in Figure 3B. The amorphous SiNPs confirmed the presence of Si and O and the absence of any other impurities, thus validating the purity of the product obtained as depicted (Figure 3C). The crystalline SiNPs denoted small peaks for Na and S, which could be due to traces of residual elements left in the process of washing (Figure 3D).

3.3. Fourier Transform Infrared Analysis

The Fourier transform IR analysis samples were recorded in the spectrum range of 4000–500 cm⁻¹. FTIR of RSAs, presented in Figure 4, showed significant bands at 794 cm⁻¹, 1109 cm⁻¹ corresponding to the symmetric and asymmetric stretching vibration of the Si−O−Si bond [6,12]. The peak observed for RSA-600 at 991 cm⁻¹ signified the Si−OH bond’s bending vibration that diminished completely for RSA-900 [34]. The bonds 1629 cm⁻¹ and 3448 cm⁻¹ indicated the bending and stretching vibration of the H−OH bond. The results are indicated in (Figure 4A,B). FTIR analyses of synthesized SiNPs showed broadband ranged between 3000–3500 cm⁻¹ that indicated the presence of silanol group (Si−OH) bonding. The little band in the region of 1633 cm⁻¹ corresponded to the bending vibrations of H−O−H (water molecules). The dominant peak at 1097 cm⁻¹ was due to the asymmetric vibration of the Si−O−Si bond. The band at 789 cm⁻¹ corresponded to Si−O−Si bond stretching [13,35], as shown in Figure 4C,D. A comparison of the spectral values obtained, and literature reports are briefly outlined in

Table 1. Infrared bands observed in ashes (RSA-600, RSA-900), SiNPs (amorphous and crystalline).

RSA-600	RSA-900	SiNPs (Amorphous)	SiNPs (Crystalline)	Literature	Functional Groups
459	470	462	452	460 [36]	Si−O
1091	11,081	1073	1101	1033 [12]	Si−O−Si
3474	3421	3423	NA	3000–3500 [13]	Si−OH
NA	NA	1663	1641	1600 [35]	H−OH
795	775	796	817	796 [6]	Si−O−Si

RSA 600—Rice straw ash obtained at 600 °C; RSA 900—Rice straw ash obtained at 900 °C; SiNPs—Silica nanoparticles.

.

3.4. Morphology Studies

FE-SEM analysis of RS showed a stable, well-defined structure (Figure 5A). The microscopic analysis of RS ash (RSA-600 and RSA-900) showed a homogeneous distribution of dumbbell-shaped phytoliths commonly referred to as silica bodies over the entire surface (Figure 5B,C). The TEM analysis of RSAs showed the agglomeration of small circular bodies over the entire surface (Figure 5D,E).

FE-SEM analysis of amorphous SiNPs synthesized by RSA-600 depicted the particles of spheroid morphology with loose aggregates compared to crystalline SiNPs synthesized by RSA-900 (Figure 5F,G). The formation of aggregates could be attributed to the gel-like property of the hydrated silica and its high surface area [7,11,12]. TEM analysis revealed the amorphous SiNPs to be spherical, with the average particle size of 27.47 nm possessing little agglomeration. In contrast, crystalline SiNPs possessed average particle size of 52.79 nm with high agglomeration (Figure 5H,I). The results obtained can be well attested by the findings of Bahrami et al. [10] and Lu et al. [6] where it was postulated that high temperature leads to the formation of crystalline silica, keeping the Si bonds intact.

3.5. Surface Area and Porosity Studies

BET analysis revealed that amorphous SiNPs possessed a specific surface area (SSA) of 226.811 m²/g with an average pore volume of 1.144 cm³/g, whereas the crystalline SiNPs had a BET SSA of 84.45 m²/g with a pore volume of 0.497 cm³/g. Nitrogen adsorption-desorption isotherm for the amorphous and crystalline SiNPs are shown in Figure 6A,B. The results were in line with the findings of Beidaghy Dizaji et al. [37] who documented that the porosity of silica-rich ashes diminish once the crystallinity fraction is higher than 10 wt.%. Didamony et al. [38] reported a surface area of 160 m²/g from SiNPs extracted using sodium silicate solution, while Yuvakumar et al. [39] reported the amorphous synthesized SiNPs with a surface area of 274 m²/g and an average pore diameter of 1.46 nm.

The results attested the findings that the amorphous SiNPs had significantly better attributes when compared to the crystalline SiNPs, thus increasing its utility in industrial sectors.

3.6. Decolorization of Cationic Dye Methylene Blue Using Amorphous SiNPs

The photocatalytic degradation studies tested the effect of different concentrations of SiNPs on a constant concentration of methylene blue dye (100 ppm). The studies reflected that the dye was efficiently degraded by 66.26% within the first 10 min by the SiNPs at 50 ppm concentration. Degradation of the dye at the lowest SiNPs concentration of 10 ppm did not reveal any observable degradation pattern. It showed a similar trend as to the degradation process without SiNPs (Figure 7A). This could be possibly explained owing to the availability of fewer adsorption sites of SiNPs at a relatively high concentration of dye. Decolorization of ~100% was achieved within the initial 30 min of the study for the dye treated with SiNPs.

The result obtained could be well correlated to the effect of UV-C irradiation that assisted in the induction of the direct photolysis on the dye. Moreover, as the UV-C photons have a shorter penetration potential through photocatalyst particles, the possibility of electron-hole recombination is minimized due to shorter travel distances, leading to higher photocatalytic activity [27,29,40]. The high surface area of amorphous SiNPs accelerated the degradation process. A comprehensive detail of dye decolorization documented by numerous researchers using SiNPs is highlighted in

Table 2. Nanosilica in photocatalytic degradation of textile dye effluents.

Dye	Concentration (Dye) and pH	Source of SiNPs	Concentration (Nanosilica)	Source	Degradation (%)	Time	References
Crystal Violet	50 mg/L; pH 7	Rice husk	1 g/L	Ultrasound	80%	60 min	Peres et al. [41]
Methyl red	0.05 Mm/100 mL; pH 7	Rice husk	1 g/100 mL	Sunlight	95%	120 min	Vinoda et al. [42]
Methylene blue	50 ppm/50 mL; pH-not reported	Rice husk	50 mg/100 mL	Ceramic material based on amorphous SiNPs	80%	30 min	Tolba et al. [25]
Methylene blue	100 mg/L; pH 11	Yellow sand	10 g/L	Ultraviolet light	100%	90 s	Aly and Elhamid [26]
Methylene blue	50 ppm; pH 7	ZnO/SiO2 xerogel	0.075 g/L	Visible light	100%	30 min	Stanley [27]
Acridine orange	1 × 10−5 M	3-aminopropyl-functionalized silica NPs	10 mg/3 mL	Ultraviolet light	58%	50 min	Selvaggi et al. [43]
Acid ornage	150 mg/L	Sugar cane ash	1 g/L	Not reported	80%	30 min	Rovani et al. [44]
Malachite green	20 mg/L; pH 9	Fe3O4@SiO2-COOH NPs	0.5 g/L	Not reported	97.5%	120 min	Galangash et al. [45]

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3.6.1. Mechanism of Photocatalytic Degradation of Methylene Blue Using SiNPs

The mechanism of photocatalytic activity can be explained owing to the ability of SiNPs to be photoexcited under UV irradiation. This phenomenon can be supported by the charge transfer from Si−O bonding orbital to 2p non-bonding orbital of non-bridging oxygen. Interestingly, as observed in FTIR studies, the presence of Si−O and Si−OH groups imparts a negative charge on the silica surface, thus offering the SiNPs to serve as an excellent medium for adsorbent cationic dyes [43,46].

On striking the surface of SiO₂ by UV light, an electron transfer occurs from the valence band to the conduction band, generating a positive hole in the valence band (v_b) and a negative hole in the conduction band (c_b), leading to the formation of active photocatalytic centers on the surface of SiNPs (Equation (1)). The v_b hole further interacts with chemisorbed H₂O molecules to form OH radicals that successively attacks dye molecules (Equation (2)). The generation of heat in this process could be ascribed due to the combination of e_cb⁻ and h_vb⁺ on the particle’s surface. A plausible cause for dye decolorization can be attributed to the hydroxyl attack and conduction of the experiment at high pH, increasing OH⁻ groups on the silica surface, leading to an acceleration of dye degradation process [25,47].

A diagrammatic sketch of the mechanism is shown in Figure 7B.

SiO₂ + hv → e_cb⁻ + h_vb⁺

(1)

HO₂ + OH⁻ + h_vb⁻ → OH

(2)

The e_cb⁻ and h_vb⁺ recombine on the particle’s surface within nanoseconds, and the generated energy becomes dissipated in the form of heat. e_cb⁻ further reacts with the acceptor dissolved O₂ and is transformed to a super oxide radical anion (O₂^·−), leading to the further growth of O₂H molecules (3):

O₂ + e_cb⁻ → O₂^−· + (H⁺ + ⁻OH) → HO₂ + OH⁻

(3)

h_vb⁺ interacts with the donor ⁻OH and ^·O₂H forming ^·OH radical that attacks the MB in the following manner:

HO₂^· + OH⁻ + h_vb⁻ → ^·OH

(4)

The governing factor monitoring the efficiency of SiNPs is the amount of ^·OH radicals generated. Since the hydroxyl groups on the SiNPs surface are attached to the silicon atom, they are termed as silanols. The OH groups present in the silanols can preferentially complex particular chemicals or metal ions, imparting functionality to SiNPs [48]. It is worth highlighting that shifting the pH towards the alkaline range led to a dramatic boost in dye degradation. Henceforth, varying the pH value can significantly impact the interactions of various compounds with silanols. Subsequently, any factor that contributes to the generation of ^·OH radicals lead to an enhancement in the photocatalytic degradation process of methylene blue.

3.6.2. Kinetic Study of Dye Degradation

Kinetic studies were performed for the optimal concentration of SiNPs (50 ppm) that aided in the complete degradation of the methylene blue dye compared to the dye treated under UVC. The effect of SiNPs on dye decolorization indicated first-order kinetics. The linear form of the first-order rate equation is denoted by Equation (5), and the half-life (t_0.5) of dye decolorization was calculated using Equation (6) [47]:

ln D_Ab = −kt + ln D_A0

(5)

t_0.5 = 0.693/k

(6)

where D_Ab is the dye absorbance at different incubation times, k is decolorization rate constant, D_A0 is the initial absorbance of the dye, and t_0.5 is the time required to decolorize 50% dye.

The logarithm plot of dye concentration vs. treatment time with SiNPs exhibited a rate constant (k) of 0.102 min⁻¹ and t_0.5 of 6.79 min. In contrast, the untreated dye exhibited a rate constant of 0.044 min⁻¹ and t_0.5 of 15.75 min, reported for the 30 min study. The results obtained thus positively attest to the enhanced effect in dye degradation due to incorporation of the SiNPs as shown in Figure 7C.

3.6.3. FTIR Studies of Methylene Blue Decolorization

The methylene blue molecular structure transformation was further evaluated by the FTIR analysis of the treated and untreated samples. UV-Vis spectra illustrated the presence of aromatics along with conjugates of N–S heterocycle group and phenothiazine structure [29]. The results in Figure 8 showed that the broad peak at 3451 cm⁻¹ was determined as the O−H stretching vibration of water molecules. It could be seen that the peak corresponding to C−H absorption of benzene ring occurred at 2975 cm⁻¹. The peak at 2105 cm⁻¹ denoted the stretching vibration peak of the methyl group. The C=C framework corresponding to benzene ring vibration and the C=N stretching vibration was found at 1646 cm⁻¹. The absorption peak at 1420 cm⁻¹ was related to another typical vibration in methyl bending. Other prominent peaks were in the vibration of C=O and -C-C at 1206 cm⁻¹ and 991 cm⁻¹. It was noticed that the intensity of absorption peaks for C=N and O−H had significant decrease in C=C aromatic stretch in the treated sample, indicating a change in chemical composition. This could be possibly attributed to the breakdown of the N−S heterocyclic compound during the degradation process [25,26,49]. The characteristic peak of benzene and C−H bending vibration of aromatic C−H declined substantially, indicating the variation in chemical compositions of phenyl groups.

It henceforth can be deduced from the spectra that the adsorption of methylene blue on the surface of SiNPs led to a remarkable change in infrared bands intensities, retaining its positions.

Stanley [26], Salimi [40] and Singh [43] hypothesized that the conjugate structure of N−S heterocyclic underwent variations in chemical composition, and consequently the aromatic ring was oxidized to open the ring leading to degradation of the dye molecules during the photocatalysis reaction. The result obtained provides new insight into potential waste usage and utilizing the low-cost synthesized SiNPs for dye degradation.

4. Conclusions

The study revealed that RS combusted at 600 °C served as an ideal condition for synthesizing amorphous SiNPs. The findings and characterization postulated that the amorphous SiNPs served better attributes when compared to crystalline SiNPs, establishing that all the researchers/stakeholders working in this domain can note that lower temperature offers a more sustainable route in product synthesis. This first-hand analysis provided the particulars pertaining to temperature’s crucial role and effect on the characterization and properties of SiNPS. The efficacy of the green synthetic route for amorphous SiNPs holding potential applications in different sectors was accessed in the field of wastewater and textile effluents for degradation of the toxic dye methylene blue. Additionally, incorporating microwave, sonication, conjugation of substrates as laccase, surface modification of SiNPs can further be attempted towards the dye degradation process. However, the study has much to offer in terms of optimizing the synthesis process via integrating surfactants, catalyst, residence time, etc., to enhance the surface area and pore size of SiNPs; that will further assist in the degradation process with a minimal dose of SiNPs and enhancing its utility as an adsorbent in different industrial sectors. Contemplating the abundance of agro-waste RS worldwide, the study establishes a background in converting the waste to a value-added product, providing a comprehensive and viable sustainable resolution towards stubble burning to achieve the SDGs 3, 7, 8 and 13.