Spectrophotometric Determination of Amaranth Dye Using a Two-Step Green Cloud Point and Magnetic Solid-Phase Extraction Approach

: The present study introduces a two-step extraction methodology that integrates cloud point extraction (CPE) with magnetic solid-phase extraction (MSPE) for the extraction and quantiﬁcation of amaranth dye. Initially, the dye is extracted using CPE in the micellar phase of the non-ionic surfactant Triton X-114. Subsequently, hydrophobic tetraethyl orthosilicate (TEOS)-modiﬁed Fe 3 O 4 magnetic nanoparticles (MNPs) are employed to recover the micellar phase. A comprehensive evaluation was conducted to optimize the key parameters inﬂuencing the efﬁcacy of both CPE and MSPE techniques, as well as signal enhancement. Under optimized conditions, the proposed methodology exhibited a linear response in the concentration range of 10 to 90 µ g Kg − 1 , with a correlation coefﬁcient ( R 2 ) of 0.9945. The detection limit was determined to be 8.443 µ g g − 1 . This robust and environmentally friendly approach offers a promising avenue for the accurate and efﬁcient determination of amaranth dye in various applications.


Introduction
Amaranth (E-123) is a typical anionic azo dye extensively employed as a food coloring agent in various applications such as foodstuffs, cosmetics, medicines, synthetic fibers, and food additives.It is particularly used to give a vibrant red hue to various beverages.The excessive presence of amaranth azo dye in food products poses significant health risks, including genotoxicity, tumors, allergies, respiratory issues, and cytotoxicity [1,2].The chemical structure is as shown in Figure 1.
Given these health implications, it is crucial to develop precise analytical methods for the determination of amaranth azo dye in food samples to ensure both food quality and consumer health safety.Several analytical techniques, including high-performance liquid chromatography (HPLC), voltammetry spectrometry, capillary electrophoresis, and electrochemical methods, have been widely employed for this purpose [3][4][5][6][7][8][9].However, these methods often encounter two primary limitations: the first being the lower analytical sensitivity compared to the quantitative limits of the methods, and the second being the potential interference from other chemical species present in the samples.To address these issues, preconcentration techniques such as ion exchange (IE), solid-phase extraction (SPE), solvent extraction (SE), and cloud point extraction (CPE) have been utilized [10][11][12][13][14][15][16][17][18][19][20].Cloud point extraction (CPE) is considered an environmentally friendly alternative to conventional liquid-liquid extraction (LLE) methods.It offers advantages such as a high enrichment factor, reduced usage of toxic reagents, smaller sample sizes, and the elimination of large volumes of organic solvents.Furthermore, it employs non-toxic surfactants, making the method simpler, safer, and more economical [21].Combining extraction methods can be advantageous in overcoming specific limitations inherent to individual techniques, thereby saving time and enhancing selectivity [22].The objective of this study is to prepare Fe 3 O 4 nanocomposites, encapsulate them with tetraethyl orthosilicate (TEOS), and utilize them as adsorbents to improve the extraction efficiency of amaranth dye under optimized conditions of acidity, time, and temperature required for cloud point extraction.

Apparatus
A Jasco 7850 UV-Visible Spectrophotometer equipped with a 1 cm (0.5 mL) quartz cell was utilized for recording the absorption spectrum and absorption measurements.To expedite the phase separation process, a 3D device operating at 4000 rpm from UromAzma Corporation was employed.pH measurements were conducted using a Metrohm 632 pH meter with an integrated glass pH electrode.All measurements were carried out at the University of Al-Qadisiyah.

Chemicals
No additional purification was required for any of the chemicals and reagents used in this study.The azo dye, amaranth, also known as trisodium 2-hydroxy-1-(4-sulphonato-1naphthylazo)naphthalene-3,6-disulphonate (molecular formula C 20 H 11 N 2 O 10 S 3 Na 3 , molecular weight 604), was purchased from M/s Merck.A 0.1g sample of the dye was weighed and dissolved in 10 mL of ethanol in a 100 mL volumetric flask.The volume was then made up to 100 mL with distilled water to prepare a stock solution of 1000 mg/L amaranth.Distilled water was used consistently throughout the study.For the absorbance measurements of amaranth dye solutions, a Shimadzu UV-1601PC spectrophotometer set at a wavelength of 520 nm was employed.

Synthesis of TEOS Functionalized Magnetic Nanoparticles
Magnetic nanoparticles (MNPs) were synthesized using the chemical co-precipitation method.FeCl 3 • 6H 2 O (11.68 g) and FeCl 2 • 4H 2 O (4.30 g) were dissolved in 200 mL of deionized water under a nitrogen atmosphere and stirred vigorously at 85 • C. Subsequently, 20 mL of 25% aqueous ammonia solution was added, causing the solution color to change from orange to black instantaneously.The magnetic precipitate was washed twice with deionized water and once with 0.02 mol L −1 sodium chloride solution.The resulting magnetic suspension was transferred to a 250 mL round-bottom flask and allowed to settle.A strong external magnet was used to isolate the Fe 3 O 4 nanoparticles, and the supernatant was discarded.The MNPs were then coated with TEOS by adding an aqueous solution of TEOS (10%, v/v, 80 mL) and glycerol (60 mL).The mixture was stirred and heated at 90 • C for 2 h under a nitrogen atmosphere.

Recommended Extraction Procedure
In a 10 mL test tube, 2 mL of 10 mg/L amaranth dye solution was combined with 2 mL of the surfactant Triton X-114 and 1 mL of a buffer solution at pH 3. The volume was then made up to the mark with ion-free distilled water.The test tube was placed in a water bath at 40 • C for 15 min until turbidity formed.Subsequently, the tube was centrifuged for 3 min to separate the organic layer from the aqueous layer.The organic layer was then collected, and 0.05 g of the nanomaterial was added.The mixture was sonicated for 5 min, after which the nanomaterial was removed using a magnet.Two mL of ethanol was added, and the solution was sonicated for an additional 15 min.Absorbance measurements were taken at a wavelength of 520 nm.A blank was prepared in a similar manner but without the presence of dye.

Fourier Transform Infrared Spectroscopy (FTIR) Analysis
FTIR analysis was conducted for both unmodified Fe 3 O 4 magnetic nanoparticles and TEOS-modified Fe 3 O 4 magnetic nanoparticles.For the unmodified Fe 3 O 4 nanoparticles, the FTIR spectrum was obtained using the KBr (potassium bromide) disc method and is depicted in Figure 2. The spectrum was recorded within the wavenumber range of 400-4000 cm −1 .The FTIR data for the unmodified Fe 3 O 4 nanoparticles are presented in Figure 2 and Table 1 which serves as a baseline for comparing the effects of TEOS modification.The wave numbers observed for Fe 3 O 4 are contingent upon the spectroscopic technique employed for analysis.Infrared spectroscopy is frequently used to study the vibrational modes of molecules, with wave numbers typically reported in units of reciprocal centimeters (cm −1 ).The infrared spectrum of Fe 3 O 4 generally exhibits several bands in the range of 400-4000 cm −1 , corresponding to different vibrational modes within the iron oxide lattice.These wave numbers can vary based on sample preparation and measurement conditions.Some typical wave numbers for Fe 3 O 4 in the infrared region include Note that these wave numbers are approximate and may vary depending on the specific sample.
The FTIR data for Fe 3 O 4 nanoparticles after TEOS coating are presented in Table 2 and Figure 3.The spectrum reveals several new peaks compared to the uncoated Fe 3 O 4 , indicating successful modification.Notably, the appearance of peaks at 1058 cm −1 and 850 cm −1 can be attributed to Si-O-Si and CH 3 -Si-O-bonds, respectively, confirming the presence of TEOS on the Fe 3 O 4 surface.The FTIR spectrum of TEOS-coated Fe 3 O 4 is expected to contain absorption peaks corresponding to both TEOS and Fe 3 O 4 , as well as any functional groups that may be present on the surface of the nanoparticles.Below are some typical FTIR wavenumbers for TEOS and Fe Note that the exact wavenumbers and peak shapes can vary depending on factors such as the synthesis method, the size and shape of the nanoparticles, and any surface modifications that may have been applied.

Transmission Electron Microscopy (TEM)
Transmission Electron Microscopy (TEM) offers highly detailed insights into the structure and composition of materials, including aspects such as crystal structure, defects, grain boundaries, and surface features.
Figure 4 presents the TEM analysis of Fe 3 O 4 nanoparticles.The particles were observed to have a size range of 50-100 nm and were nearly spherical in shape, consistent with previous studies.The intensity and full-width at half maxima (FWHM) of these peaks can provide information about the size and degree of crystallinity of the Fe 3 O 4 nanoparticles (Figure 6).Smaller particle sizes result in broader diffraction peaks and lower peak intensity.Peak broadening may also indicate a degree of disorder within the crystalline structure of the nanoparticles.In the XRD spectrum of Fe 3 O 4 -TEOS nanocomposites (Figure 7), two sets of diffraction peaks were observed.The first set, similar to that of pure Fe 3 O 4 , corresponds to its crystalline phase.The second set shows a broad hump at 2θ angles around 20 • -25 • , representing the amorphous phase of TEOS.Overall, the XRD spectrum of Fe 3 O 4 -TEOS nanocomposites confirms the presence of both crystalline and amorphous phases, suggesting that the nanocomposites comprise both crystalline and non-crystalline regions.The relative intensity of the peaks for each component can offer insights into the composition and morphology of the nanocomposites.The influence of pH, ranging from 2 to 9, was investigated using various acetate buffer solutions.The results are depicted in Figure 8.At pH 3, maximum absorption was observed.Subsequent increases in pH led to decreased absorption due to partial dissociation at higher pH levels.Therefore, pH 3 was selected as the optimal pH for dye adsorption at the wavelength of maximum absorption, 520 nm.

Effect of Time
The optimal time for measuring dye absorbance was investigated over a range from 5 to 25 min using Triton X-114 solution.The results are presented in Figure 9. Absorption initially increased with time, peaking at 15 min, and then decreased due to partial dissociation at longer times.Consequently, 15 min was chosen as the optimal time for measuring absorbance at 520 nm.

Effect of Temperature
The impact of temperature, ranging from 30 to 90 • C, was studied using solutions of dye and Triton X-114.As shown in Figure 10, absorption initially increased with temperature, reaching a peak at 40 • C. Beyond this point, absorption decreased due to partial dissociation at higher temperatures.Therefore, 40 • C was selected as the optimal temperature for dye adsorption at 520 nm.

Analytical Performance of the Optimized Method
Under optimal conditions, the calibration curve was linear over a concentration range of 10-90 µg Kg −1 with a correlation coefficient (R 2 ) of 0.9945.Calibration curve solutions were prepared by spiking appropriate amounts of amaranth dye working solutions and subjected to the recommended CPE-MSPE procedure.The limit of detection (LOD), calculated as 3.3 × S b /m (where S b is the standard deviation of nine replicate measurements of a blank solution, and m is the slope of the calibration curve), was found to be 8.443 µg g −1 .

Conclusions
The integration of Cloud Point Extraction (CPE) with Tetraethyl Orthosilicate (TEOS)modified Fe 3 O 4 Magnetic Solid-Phase Extraction (MSPE) has been effectively utilized as a proficient sample pretreatment procedure for the extraction and determination of amaranth dye.This analytical methodology offers several advantages such as operational simplicity, minimal organic solvent consumption, and a high pre-concentration factor.Furthermore, the developed approach demonstrates a competent capability for the detection of trace amounts of amaranth dye in various samples, showcasing its potential applicability in ensuring the quality and safety of products containing amaranth dye.

• 579 cm − 1 :
stretching vibration of Fe-O bonds.• 670 cm −1 : bending vibration of Fe-O bonds (not observed in this study).• 1100-1200 cm −1 : stretching vibration of the O-Fe-O bridges in the spinel structure (not observed in this study).• 1623 cm −1 : bending vibration of the O-Fe-O bridges in the spinel structure.• 3398 cm −1 : O-H stretching, associated with water molecules adsorbed on the surface of Fe 3 O 4 .

Figure 4 .
Figure 4. Transmission Electron Microscopy image of Fe 3 O 4 nanoparticles.Upon coating Fe 3 O 4 with TEOS, a distinct change in morphology was observed, as shown in Figure 5.The dark-colored nanoparticles represent the Fe 3 O 4 core, while the lighter-colored particles indicate the TEOS coating.The image reveals that the TEOS surface is densely covered by uniformly distributed Fe 3 O 4 nanoparticles, indicating a significant agglomeration of Fe 3 O 4 particles on the TEOS surface.

Figure 8 .
Figure 8.Effect of pH on the adsorption of the organic layer of amaranth dye.Conditions: 1 mL of dye, 2 mL of Triton X-114.

Figure 9 .
Figure 9.The effect of time on the adsorption of the organic layer of amaranth dye.Conditions: 2 mL of dye, 2 mL of Triton X-114, pH 3.

Figure 10 .
Figure 10.The effect of temperature on the adsorption of the organic layer of amaranth dye.Conditions: 2 mL of dye, 2 mL of Triton X-114, pH 3, temperature 40 • C, time 15 min.3.4.4.Effect of Amount of Nanomaterials TEOS-modified Fe 3 O 4 -NPs were added to the sample solution in amounts ranging from 0.01 to 0.06 g.As shown in Figure 11, the extraction efficiency improved up to 0.05 g of adsorbent.Due to the high surface-to-volume ratio of the nanoparticles, accurate extraction could be achieved with a minimal amount of adsorbent.Consequently, 0.05 g was selected for further experiments.

Figure 11 .
Figure 11.The effect of the amount of nano material on the adsorption of the organic layer of the dye.Conditions: 2 mL of dye, 2 mL of Triton X-114, pH 3, temperature 40 • C, time 15 min.

Table 2 .
FTIR data for Fe 3 O 4 nanoparticles after TEOS coating.