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Original Article
ARTICLE IN PRESS
doi:
10.25259/AJC_855_2025

Simultaneous determination of triazine-based UV absorbers by first-order derivative spectrophotometry in different media

State Key Laboratory of New Textile Materials and Advanced Processing, Wuhan Textile University, Wuhan, P. R. China
School of Chemistry and Environmental Engineering, Wuhan Institute of Technology, Donghu New & High Technology Development Zone, Wuhan, PR China
School of Chemistry and Chemical Engineering, Hubei Polytechnic University, Huangshi, PR China
MFCI Technology Development Co., Ltd., Wuhan, PR China
MFCI (Huangang) Co., Ltd.), Huanggang, PR China
Authors contributed equally to this work and shared co-first authorship.

* Corresponding author: E-mail address: rchenhku@hotmail.com (R. Chen)

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This is an open-access article distributed under the terms of the Creative Commons Attribution-Non Commercial-Share Alike 4.0 License, which allows others to remix, transform, and build upon the work non-commercially, as long as the author is credited and the new creations are licensed under the identical terms.

Abstract

The simultaneous determination of individual components in mixtures of UVA- and UVB-type triazine-based UV absorbers, including bis-ethylhexyloxyphenol methoxyphenol triazine (BEMT), diethylhexyl butamido triazone (DBT), and ethylhexyl triazone (EHT), presents significant challenges due to the strong spectral overlap in their UV absorption profiles. In this study, we explored the feasibility of employing first-derivative spectrophotometry for the simultaneous quantitative determination of these UV absorbers in a variety of organic solvents, such as chloroform, diethyl ether, ethyl acetate, acetonitrile, dimethyl sulfoxide (DMSO), 1,4-dioxane, isopropanol, etc. Focusing on quality control analysis during sunscreen formulation, a first-order derivative spectrophotometric method was developed for quantifying binary mixtures in dioctyl carbonate, a commonly used solvent in sunscreens. For the binary mixture BEMT-DBT and BEMT-EHT, the optimal wavelengths for quantification were identified as 372 nm for BEMT, 316 nm for DBT, and 318 nm for EHT, respectively. This method demonstrated a linear relationship within the concentration range of 1 to 9 mg L-1 for both systems. In the BEMT-DBT mixture, the mean recoveries were documented at 98.96±1.54% for BEMT and 100.84±2.28% for DBT. The average relative standard deviations (RSD) for both intra-day and inter-day precision remained below 2.47%. In the binary mixture BEMT-EHT, the mean recoveries for BEMT and EHT were 98.43±2.10% and 99.85 ± 1.68%, respectively. Additionally, the average RSD values for both intra-day and inter-day precision remained below 1.46%. To facilitate quantitative analysis of triazine-based UV absorber mixtures for the studies concerning their sorption behavior and ecotoxicity in aqueous environments, this method was successfully adapted in a DMSO/H₂O (4:96, v/v) mixed solvent system. This adaptation enabled effective simultaneous determination of both BEMT-DBT and BEMT-EHT binary systems within this medium.

Keywords

bis-ethylhexyloxyphenol methoxyphenol triazine
diethylhexyl butamido triazone
Derivative spectrophotometry
ethylhexyl triazone
Quantitative analysis

1. Introduction

Triazine-based UV absorbers are a relatively new class of sunscreen agents that have gained considerable popularity in recent years. The primary compounds within this category include bis-ethylhexyloxyphenol methoxyphenyl triazine (BEMT), diethylhexyl butamido triazone (DBT), and ethylhexyl triazone (EHT). These compounds exhibit strong light photo-stability, excellent durability [1], and limited dermal absorption, rendering them suitable for children’s sunscreens [2,3]. In South Korea, BEMT was present in 42% of sunscreen products, while EHT usage increased significantly from 4% during 2016-2017 to 30.7% in 2024 [4]. In France, EHT is included in 57% of commercially available sunscreen products [5]. Triazine-based UV absorbers are commonly incorporated into personal care products in South America [6]. To achieve broad-spectrum UV protection, UVA- and UVB-type triazine-based UV absorbers are typically combined in sunscreen formulations [7,8]. Notable combinations include BEMT with EHT or DBT. The chemical structures of these UV absorbers have been detailed in Table S1.

Table S1

Triazine-based UV absorbers enter aquatic environments through direct pathways [9], such as swimming and bathing, as well as indirect routes including sewage discharge [10]. Owing to their high octanol/water partition coefficient [11], the concentrations of triazine-based UV absorbers typically occur at trace levels in aquatic environments, often below the detection limits of current monitoring technologies. This situation impedes the monitoring endeavors of existing sewage treatment facilities. These compounds exhibit low water solubility, high stability, and a propensity for bioaccumulation, enabling their persistence in sediments and greywater runoff [12], and leading to long-term environmental accumulation [13,14]. Therefore, there is an urgent need for rapid and accurate detection methods capable of identifying trace triazine-based UV absorbers in diverse aquatic matrices.

To date, various analytical methods have been developed for the determination of triazine-based UV absorbers, including ultraviolet spectrophotometry [15,16], Frontal thin-layer chromatography-density measurement [17], high-performance liquid chromatography (HPLC) [18-20], high-performance liquid chromatography mass spectrometry (HPLC-MS) [21,22], and gas chromatography-mass spectrometry (GC-MS) [23]. Among these techniques, HPLC is predominantly used for analyzing mixtures of triazine-based UV absorbers; however, it exhibits notable limitations, including high cost and slow processing times, which impede rapid concentration assessment in mixed samples, particularly in field or outdoor settings. Consequently, the development of fast and practical analytical methods is critical for environmental risk evaluation. Although conventional UV spectrophotometry is convenient and widely utilized, it lacks the specificity to quantify individual components in complex mixtures with overlapping absorption spectra.

Derivative UV spectrophotometry effectively overcomes this limitation of spectral overlap interference, thereby facilitating the specific quantitative analysis of individual components in multi-component systems [24-26]. Through mathematical differentiation, this technique converts UV absorption spectra into derivative spectra characterized by distinct features, such as zero-crossing points, where peak maxima correspond to zero derivatives or distinct extrema. In cases of overlapping absorption bands, the derivative spectra provide unique discriminative characteristics, including variations in zero-crossing positions, slopes at extremum points, and peak widths. Quantification can be achieved by selecting a wavelength at which the derivative value of the interfering component is zero, thereby allowing the derivative response to originate exclusively from the analyte of interest. This approach effectively eliminates spectral interference from overlapping peaks and enables precise quantification of the target component [27,28]. As the differentiation is a linear operation, the method adheres to the additivity principle of concentration: the derivative signal of a mixture equals the linear superposition of its derivative spectra of individual components scaled according to their respective concentrations. Hence, derivative spectrophotometry is particularly effective for resolving overlapping absorption spectra in multi-component mixtures and can be successfully employed for the quantitative determination of analytes within complex mixtures. This technique allows for optimal wavelength selection, thus improving quantitative analytical capabilities. Compared to conventional spectrophotometric methods, it offers enhanced sensitivity, selectivity, and accuracy. Furthermore, it has been extensively applied across various fields, such as pharmaceutical analysis [29,30], environmental monitoring [31,32], and biochemistry.

The solvent environment significantly influences the peak shape, sensitivity, and resolution of derivative spectra. Various solvent systems exhibit distinct physicochemical properties (such as polarity, hydrogen bond donor/acceptor capabilities, dipole moment, etc.), resulting in diverse interaction mechanisms with hydrophobic compound molecules. The triazine-based UV absorbers in this study, as typical hydrophobic compounds, may exist in the aqueous phase, adsorb onto particulate matter, deposit within environmental matrices, or accumulate in the fatty tissues of organisms in real-world environments. Water-organic mixed solvent systems (e.g., water-dimethyl sulfoxide (DMSO), water-isopropanol, water-tetrahydrofuran (THF), etc.) can effectively boost the solubility of hydrophobic compounds while maintaining a certain degree of an aqueous environment. Therefore, they are promising candidates for use as solvent systems. Moreover, in the realm of industrial production, derivative spectrophotometry is capable of swiftly monitoring, either online or in situ, the concentration fluctuations of specific hydrophobic products within reaction systems. This enables prompt modifications to process parameters, thereby guaranteeing product quality and maximizing reaction yield.

Consequently, this study aims to systematically investigate the effects of various mixed solvent systems on the spectral characteristics of triazine-based UV absorbers using derivative spectrophotometry. The objective is to enable selective determination in the presence of interfering components and ultimately establish analytical conditions marked by high sensitivity and selectivity. This work not only provides a reliable new method for accurately determining such hydrophobic compounds in complex environments-facilitating quantitative evaluations of adsorption behavior and aquatic toxicity associated with triazine-based UV absorbers in aqueous media-but also offers a rapid, straightforward, and cost-effective analytical technique suitable for selective quantification of specific components, real-time monitoring and quick decision-making in production settings, thereby ensuring product quality and environmental safety.

2. Materials and Methods

2.1. Reagents and instruments

Reference substances of BEMT, DBT, and EHT were generously provided by MFCI Co., Ltd. (Huanggang, China) and were used as received without further purification. Medium polarity organic solvents included dioctyl carbonate, chloroform, ethyl acetate, methyl tert-butyl ether (MTBE), and diethyl ether. The polar organic solvents comprised N, N-dimethyl formamide (DMF), DMSO, 1,4-dioxane, tetrahydrofuran (THF), acetonitrile, and isopropyl alcohol, etc. These reagents were sourced from Chemical Reagent in Shanghai, China, all of which are of analytical grade purity. Deionized water was obtained using a Milli-Q system from Millipore (Millipore, USA). An AOELAB A690 UV spectrophotometer equipped with a quartz cell with a 1 cm path length was employed for this study.

2.2. Experimental method

2.2.1. Configuration of standard and mixing solution

Preparation of single-component stock and standard solutions: A range of single-component standard stock solutions was prepared using different solvents. Specifically, precisely weigh and transfer 500 mg each of BEMT, EHT, and DBT into individual 500 mL brown volumetric flasks, then dilute them to the calibration mark to achieve standard stock solutions of the three triazine-based UV absorbers, each with a concentration of 1000 mg L-1. The prepared standard stock solutions were securely sealed in a refrigerator at 4°C. Utilizing these standard stock solutions as the mother liquor, single-component standard solutions with concentrations of 1, 3, 5, 7, 9, and 11 mg L-1 were obtained through a systematic stepwise dilution process.

Preparation of mixed stock and mixed standard solutions: Equal volumes of two single-component triazine-based UV absorber stock solutions, each having an initial concentration of 1000 mg L-1, were combined to create a mixed stock solution containing each triazine-based UV absorber at a concentration of 500 mg L-1. The dilution and preparation procedures for the mixed standard solutions followed the same methodology as that employed for the single-component standard solutions.

The solvents employed for preparing the above stock and standard solutions encompassed medium-polarity and polar organic solvents, including dioctyl carbonate, chloroform, ethyl acetate, diethyl ether, DMSO, dimethyl formamide (DMF), acetonitrile, 1,4-dioxane, isopropanol, tetrahydrofuran (THF), etc.

2.2.2. Determination by UV-vis spectrophotometry

The ultraviolet and derivative spectra of the binary mixture were acquired by scanning from 200 to 400 nm using ultraviolet spectrophotometry. A 1 cm quartz cuvette was used for the test solution, with the corresponding solvent serving as the reference. Absorbance data were collected at intervals of 1 nm.

2.3. Method validation

2.3.1. Relative standard deviation

The intraday precision (repeatability) was assessed by analyzing the single-concentration mixed solutions of BEMT-EHT and BEMT-DBT. Three repeated measurements were conducted on the same day. To evaluate the diurnal-day precision, each mixed sample solution of ultraviolet absorber was re-prepared at the same concentration level, and response values were measured in three replicates. This procedure was carried out continuously over 3 days. Intra-day and inter-day precision are expressed as relative standard deviation (% RSD). Here, SD denotes the standard deviation of the sample, and μ represents the mean value of the sample. n indicates the total number of samples, and xi refers to the samples as shown in Equation (1) and Equation (2).

(1)
RSD = SD μ ×100%

(2)
SD  = 1 n i = 1 n x i μ 2

2.3.2. Marked recovery experiment

The accuracy is determined by the recovery rate of a known quantity of UV absorbent that has been added to the sample, which serves to assess the reliability of the method. Equation (3) and Equation (4) are used to calculate the recovery rate and relative error between the measured concentration and the added concentration, respectively.

(3)
Recovery (%)= Experimental Theoretical ×100%

(4)
Error  % = Experimental-Theoretical Theoretical ×100%

2.3.3. Determination of limits of detection and quantification

Limit of detection (LOD) and limit of quantification (LOQ) indicate the lowest concentration that can be detected by a detection method and the lowest concentration that can be accurately quantified, respectively. The following are standard formulas for calculating LOD and LOQ, where σ is the standard deviation of the Y-axis intercept, and S is the slope of the calibration curve as shown in Equation (5) and Equation (6).

(5)
LOD= 3 .3σ S

(6)
LOQ= 10 .0σ S

2.3.4. Robustness and stability

The analytical conditions selected for assessing robustness encompass parameters including scanning step size, scanning speed, and temperature. Recovery rates were measured under varying analytical conditions to evaluate the sensitivity of the measurements to intentional variations in these parameters. Additionally, recovery rate measurements were conducted over a 36 h to assess the stability of the binary mixed triazine-based UV absorbers.

3. Results and Discussion

3.1. The selection of wavelengths in different media for derivative UV spectrophotometry

In this study, we initially explored the feasibility of derivative spectrophotometry for the determination of binary mixtures of triazine-based UV absorbers in pure organic solvents, which include both medium-polarity and polar solvents. Subsequently, we extended our investigation to evaluate the applicability of this method in aqueous-containing mixed solvents (polar solvent/H2O systems).

3.1.1. Determination of quantification wavelengths in pure organic solvents

To evaluate the applicability of derivative spectrophotometry for the determination of triazine-based UV absorber mixtures across different media, we initially examined the zero-order UV absorption spectra of triazine-based UV absorbers in medium-polarity organic solvents, including chloroform, diethyl ether, ethyl acetate, and methyl tert-butyl ether (MTBE). The maximum absorption wavelengths and mass absorption coefficients for BEMT, EHT, and DBT in these solvents were documented (Table S2). The first-derivative UV spectra of the triazine-based absorbers and their binary mixtures showed suboptimal performance in diethyl ether and MTBE as solvents (Figures S1 and S2). In contrast, ethyl acetate and chloroform demonstrated optimal performance as solvents. At the zero-crossing points of interfering components, the first-derivative values for the mixtures were extremely similar to those of the analytes.

Table S2

Figures S1 and S2

In ethyl acetate, the zero-order spectra of BEMT-DBT and BEMT-EHT binary mixtures (Figures 1a,b) exhibited significant spectral overlap between 260-320 nm, which hindered simultaneous quantification. As depicted in Figure 1(c) for the BEMT-DBT mixture, a zero-crossing point for BEMT was observed near 318 nm. At this specific wavelength, the first-derivative signal of the mixture remained independent of BEMT concentration and demonstrated a linear relationship solely with DBT concentration, effectively eliminating any interference from BEMT. Similarly, DBT displayed a zero-crossing point around 369 nm, where its first-derivative signal depended linearly on BEMT concentration without any interference from DBT. Consequently, wavelengths of 318 nm and 369 nm were selected for the simultaneous quantification of DBT and BEMT in the BEMT-DBT system. For the BEMT-EHT system (Figure 1d), wavelengths of 319 nm and 369 nm were designated for EHT and BEMT quantification, respectively.

Zero-order UV spectra of (a) BEMT and DBT, (b) BEMT and EHT in single and binary solution in ethyl acetate, First-order derivative UV spectra of (c) BEMT and DBT, (d) BEMT and EHT in single and binary solution (initial concentration of 5 mg L-1 for each compound).
Figure 1.
Zero-order UV spectra of (a) BEMT and DBT, (b) BEMT and EHT in single and binary solution in ethyl acetate, First-order derivative UV spectra of (c) BEMT and DBT, (d) BEMT and EHT in single and binary solution (initial concentration of 5 mg L-1 for each compound).

In chloroform, the zero-order spectra of BEMT-DBT and BEMT-EHT mixtures have been presented in Figures 2(a,b). The corresponding first-derivative spectra (Figures 2c,d) provided quantification wavelengths of approximately 315 nm for DBT/EHT and 370 nm for BEMT in both binary systems.

Zero-order UV spectra of (a) BEMT and DBT, (b) BEMT and EHT in single and binary solution in chloroform, First-order derivative UV spectra of (c) BEMT and DBT, (d) BEMT and EHT in single and binary solution (initial concentration of 5 mg L-1 for each compound).
Figure 2.
Zero-order UV spectra of (a) BEMT and DBT, (b) BEMT and EHT in single and binary solution in chloroform, First-order derivative UV spectra of (c) BEMT and DBT, (d) BEMT and EHT in single and binary solution (initial concentration of 5 mg L-1 for each compound).

Subsequently, the applicability of derivative spectrophotometry for the determination of binary mixtures of triazine-based UV absorbers (BEMT-EHT, BEMT-DBT) was assessed across various polar organic solvents, including acetonitrile, DMSO, 1,4-dioxane, isopropanol, DMF, and THF. The maximum absorption wavelengths and mass absorption coefficients for BEMT, EHT, and DBT in these solvents were documented (Table S3). The method exhibited broad applicability in most solvents examined (Figures S3-S6). Utilizing isopropyl alcohol as the solvent, the zero-order UV absorption spectra for the BEMT-DBT and BEMT-EHT binary mixtures in isopropanol have been illustrated in Figures 3(a,b). The corresponding first-derivative spectra (Figures 3c,d) yielded quantification wavelengths near 322 nm for EHT/DBT and approximately 370 nm for BEMT in both systems.

Table S3

Figures S3-S6
Zero-order UV spectra of (a) BEMT and DBT, (b) BEMT and EHT in single and binary solution in isopropanol, First-order derivative UV spectra of (c) BEMT and DBT, (d) BEMT and EHT in single and binary solution (initial concentration of 5 mg L-1 for each compound).
Figure 3.
Zero-order UV spectra of (a) BEMT and DBT, (b) BEMT and EHT in single and binary solution in isopropanol, First-order derivative UV spectra of (c) BEMT and DBT, (d) BEMT and EHT in single and binary solution (initial concentration of 5 mg L-1 for each compound).

Using DMSO as the solvent, the zero-order spectra of the BEMT-DBT and BEMT-EHT mixtures in DMSO have been shown in Figures 4(a,b). An analysis of their first-derivative spectra (Figures 4c,d) similarly revealed quantification wavelengths at approximately 322 nm for EHT/DBT and at 365 nm for BEMT.

Zero-order UV spectra of (a) BEMT and DBT, (b) BEMT and EHT in single and binary solution in DMSO, First-order derivative UV spectra of (c) BEMT and DBT, (d) BEMT and EHT in single and binary solution (initial concentration of 5 mg L-1 for each compound).
Figure 4.
Zero-order UV spectra of (a) BEMT and DBT, (b) BEMT and EHT in single and binary solution in DMSO, First-order derivative UV spectra of (c) BEMT and DBT, (d) BEMT and EHT in single and binary solution (initial concentration of 5 mg L-1 for each compound).

3.1.2. Determination of quantification wavelengths in aqueous-organic mixed solvents

To facilitate the quantitative analysis of the sorption behavior and ecotoxicity of triazine-based UV absorber mixtures in aquatic environments, we further explored the feasibility of a method utilizing various water-organic mixed solvents (polar solvent/H2O). A strong linearity between absorbance and concentration was demonstrated within these mixed solvents (Figure S7), Simultaneously, the stability of the triazine-based UV absorbers was evaluated across different mixed solvent systems, including 1,4-dioxane/H2O (4:96, v/v), methanol/H2O (4:96, v/v), acetonitrile/H2O (4:96, v/v), and DMSO/H2O (4:96, v/v) (Figures S8-S10). The viability of employing derivative spectrophotometry for determining binary mixtures of triazine-based UV absorbers in multiple polar organic/water mixed solvents was confirmed.

Figure S7

Figures S8-S10

Among the evaluated polar organic solvent/H2O (4:96, v/v) systems, isopropanol/H2O (4:96, v/v) and DMSO/H2O (4:96, v/v) demonstrated optimal analytical performance. Utilizing isopropanol/H2O (4:96, v/v) as the solvent, the zero-order UV absorption spectra of BEMT-DBT and BEMT-EHT binary mixtures have been presented in Figures 5(a,b). The corresponding first-derivative spectra shown in Figures 5(c,d) provided quantification wavelengths at 326 ± 1 nm for both EHT and DBT, and 375 ± 2 nm for BEMT.

Zero-order UV spectra of (a) BEMT and DBT, (b) BEMT and EHT in single and binary solution in isopropanol/H2O (4:96 v/v), First-order derivative UV spectra of (c) BEMT and DBT, (d) BEMT and EHT in single and binary solution (initial concentration of 5 mg/L for each compound).
Figure 5.
Zero-order UV spectra of (a) BEMT and DBT, (b) BEMT and EHT in single and binary solution in isopropanol/H2O (4:96 v/v), First-order derivative UV spectra of (c) BEMT and DBT, (d) BEMT and EHT in single and binary solution (initial concentration of 5 mg/L for each compound).

Using DMSO/H2O (4:96, v/v) as the solvent, the zero-order UV absorption spectra of the BEMT-EHT and BEMT-DBT binary mixtures are shown in Figures 6(a,b). The corresponding first-derivative spectra (Figures 6c,d) yielded quantification wavelengths of approximately 332 nm for both EHT and DBT, around 390 nm and 384nm for BEMT.

Zero-order UV spectra of (a)BEMT and EHT, (b) BEMT and DBT in single and binary solution in DMSO/H2O (4:96 v/v), First-order derivative UV spectra of (c) BEMT and EHT, (d) BEMT and DBT in single and binary solution (initial concentration of 5 mg/L for each compound).
Figure 6.
Zero-order UV spectra of (a)BEMT and EHT, (b) BEMT and DBT in single and binary solution in DMSO/H2O (4:96 v/v), First-order derivative UV spectra of (c) BEMT and EHT, (d) BEMT and DBT in single and binary solution (initial concentration of 5 mg/L for each compound).

3.2. Application of first-derivative spectrophotometry

3.2.1. Simultaneous determination of triazine-based UV absorbers in the sunscreen solvent of dioctyl carbonate

To validate the practical utility of the method, the simultaneous determination of triazine-based UV absorber mixtures was investigated in dioctyl carbonate, a solvent commonly used in sunscreen formulations. Firstly, quantification wavelengths and calibration curves were established. The zero-order UV absorption spectra for the BEMT-DBT and BEMT-EHT binary mixtures in dioctyl carbonate have been presented in Figures 7(a,b), with their corresponding first-derivative spectra shown in Figures 7(c,d). The quantification wavelengths were determined to be 316 nm for DBT and 318 nm for EHT, where the first derivative of BEMT approached zero, thereby eliminating its interference. Similarly, 372 nm was selected for BEMT as the derivatives of DBT and EHT approached zero at this wavelength, thus removing their interference.

Zero-order UV spectra of (a) BEMT and DBT, (b) BEMT and EHT in single and binary solution in dioctyl carbonate, First order derivative UV spectra of (c) BEMT and DBT, (d) BEMT and EHT in single and binary solution (initial concentration of 5 mg L-1 for each compound).
Figure 7.
Zero-order UV spectra of (a) BEMT and DBT, (b) BEMT and EHT in single and binary solution in dioctyl carbonate, First order derivative UV spectra of (c) BEMT and DBT, (d) BEMT and EHT in single and binary solution (initial concentration of 5 mg L-1 for each compound).

In dioctyl carbonate, the first-derivative spectra for both BEMT-DBT and BEMT-EHT systems at various concentrations have been presented in Figures 8(a and b), respectively. Figures 8 (c and d) illustrate the corresponding standard curves at the specified wavelength. Within the concentration range of 1 mg L-1 to 9 mg L-1, the concentrations of single-component ultraviolet absorbers in both BEMT-DBT and BEMT-EHT exhibit a good linear relationship with the derivative values of absorbance at a specific wavelength. The quantitative statistical parameters derived from this method have been summarized in Table 1. The standard curves yielded regression coefficients of R2 (BEMT) = 0.996 and R2 (EHT) = 0.989 for BEMT-EHT, as well as R2 (BEMT) = 0.999 with R2 (DBT) = 0.984 for BEMT-DBT, thereby confirming a strong linearity between derivative response and concentration through high correlation coefficients and negligible intercepts.

First-order derivative UV spectra and calibration curves in dioctyl carbonate. (a) UV spectra of the binary mixture of BEMT and DBT (1-9 mg/L). (b) UV spectra of the binary mixture of BEMT and EHT (1-9 mg/L). (c) Calibration curves for the binary mixture of BEMT and DBT. (d) Calibration curves for the binary mixture of BEMT and EHT.
Figure 8.
First-order derivative UV spectra and calibration curves in dioctyl carbonate. (a) UV spectra of the binary mixture of BEMT and DBT (1-9 mg/L). (b) UV spectra of the binary mixture of BEMT and EHT (1-9 mg/L). (c) Calibration curves for the binary mixture of BEMT and DBT. (d) Calibration curves for the binary mixture of BEMT and EHT.
Table 1. Quantitative parameters for the Binary mixture in dioctyl carbonate by the first-order derivative absorption spectra method, and precision data of BEMT-EHT and BEMT-DBT.
Binary mixture UV absorber Linearity range (mg L-1) λ (nm) Regression equation R2 Inter-dayb
Intra-dayc
Mean %RSD Day 1(n>=3) Day 2(n>=3) Day 3(n>=3) %RSD
BEMT-EHTa BEMT 1.0-9.0 372 dA/d λ=-0.00273C-0.00078 0.996 4.07 1.46 4.15 4.1 3.97 1.33
EHT 1.0-9.0 318 dA/d λ =-0.00871-0.00298 0.989 6.90 0.72 6.90 6.85 6.95 1.46
BEMT-DBTa BEMT 1.0-9.0 372 dA/d λ= -0.00307C-0.001 0.999 4.96 1.53 5.05 4.90 4.95 1.89
DBT 1.0-9.0 316 dA/d λ =-0.00834-0.00851 0.984 2.97 2.47 3.06 2.92 2.95 1.72

aTheoretical concentration: 4 mg L-1 for BEMT and 7 mg L-1 EHT. Theoretical concentration: 5 mg L-1 for BEMT and 3 mg L-1 for DBT.

bMean of determinations on 3 different days

cMean of 3 determinations

The sensitivity was determined using Eqs. (5) and (6) to calculate the values for LOD and LOQ, as presented in Table S4. LODs for BEMT and EHT in the BEMT-EHT binary system were 0.43 mg L-1 and 0.25 mg L-1, respectively, while the LOQs were determined to be 1.30 mg L-1 and 0.76 mg L-1, respectively. LODs for BEMT and DBT in the BEMT-EHT binary system were 0.38 and 0.22 mg L-1, respectively, while the LOQs were determined to be 1.15 mg L-1 and 0.67 mg L-1, respectively (Table S4). These values show that the proposed method has good sensitivity.

Table S4

Subsequently, we conducted method validation to confirm the accuracy, reliability, and applicability of this approach. The precision evaluation data for the first-derivative spectrophotometric determination of BEMT-EHT and BEMT-DBT binary mixtures in dioctyl carbonate were evaluated, as summarized in Table 1. As illustrated in Table 1, both intra-day and inter-day precision studies demonstrated relative standard deviations (RSD) below 2.47% (n=3), indicating excellent reproducibility and high precision of the method.

The accuracy assessment data for the BEMT-EHT and BEMT-DBT binary systems have been presented in Table 2. The results indicate mean recoveries of 98.13% for BEMT and 99.54% for EHT within the BEMT-EHT system, accompanied by corresponding mean relative errors of 1.87% and 0.46%. In the case of the BEMT-DBT system, mean recoveries were found to be 98.18% for BEMT and 98.01% for DBT, with mean relative errors of 1.82% and 1.99%. The close alignment between theoretical values and experimentally determined values validates the accuracy of the proposed method.

Table 2. The recovery data for the simultaneous determination of the first-order derivative UV spectrophotometric method in dioctyl carbonate.
BEMT-EHT
BEMT-DBT
Theoretical (mg L-1)
Experimental (mg L-1)
Recovery (%)
Error (%)
Theoretical (mg L-1)
Experimental (mg L-1)
Recovery (%)
Error (%)
BEMT EHT BEMT EHT BEMT EHT BEMT EHT BEMT DBT BEMT DBT BEMT DBT BEMT DBT
2.0 2.0 1.95 1.94 97.50 99.49 -2.50 -0.51 2.0 2.0 1.92 1.93 96.00 96.50 -4.00 -3.50
4.0 4.0 3.88 4.01 97.00 103.35 -3.00 3.35 4.0 4.0 3.85 3.93 96.25 98.25 -3.75 -1.75
6.0 6.0 5.94 6.11 99.00 102.86 -1.00 2.86 6.0 6.0 5.85 6.12 97.50 102.00 -2.50 2.00
8.0 8.0 8.07 7.85 100.88 98.13 0.88 -1.88 8.0 8.0 8.06 7.96 100.75 99.50 0.75 -0.50
5.0 3.0 4.95 3.08 99.00 102.67 -1.00 2.67 5.0 3.0 5.07 2.94 101.40 98.00 1.40 -2.00
3.0 5.0 2.95 5.07 98.33 101.40 -1.67 1.40 3.0 5.0 2.94 4.95 98.00 99.00 -2.00 -1.00
7.0 11.0 7.07 10.78 101.00 98.00 1.00 -2.00 7.0 11.0 6.94 10.86 99.14 98.73 -0.86 -1.27
Mean±SD BEMT=98.96±1.54 EHT=100.84±2.28 Mean±SD BEMT=98.43±2.10 DBT=98.85±1.68

3.2.2. Simultaneous determination of triazine-based UV absorbers in DMSO/H2O (4:96, v/v) mixed solvent

Due to its low toxicity and high stability, DMSO is extensively used as a cosolvent in toxicity experiments involving hydrophobic pollutants. Consequently, we concentrated on investigating the quantitative analysis of binary triazine-based UV absorbers in DMSO/H2O (4:96 v/v) mixed solvents using derivative spectrophotometry. Figures 9(a, b) present the first-derivative spectra for both BEMT-DBT and BEMT-EHT systems at various concentrations in this medium, respectively. The corresponding standard curves are depicted in Figures 9(c,d). The regression analysis confirmed excellent linearity within the established concentration range, with R2 values of 0.997 (BEMT) and 0.998 (DBT) for the BEMT+DBT system, as well as R2 values of 0.999 (BEMT) and 0.997 (EHT) for the BEMT+EHT system, thus validating the method’s efficacy for precise quantification of individual components in DMSO/H₂O (4:96, v/v) mixed systems.

First-order derivative UV spectra of the binary mixture of (a) BEMT and DBT, (b) BEMT and EHT within the concentration range of 1-11 mg L-1 in DMSO/H2O (4:96 v/v), Calibration curves for binary mixture of (c) BEMT and DBT, (d) BEMT and EHT.
Figure 9.
First-order derivative UV spectra of the binary mixture of (a) BEMT and DBT, (b) BEMT and EHT within the concentration range of 1-11 mg L-1 in DMSO/H2O (4:96 v/v), Calibration curves for binary mixture of (c) BEMT and DBT, (d) BEMT and EHT.

Table 3 shows the linear relationship between the concentrations of two two-component mixed ultraviolet absorbers in DMSO/H2O (4:96, v/v) solution and dA/dλ, which includes details on the concentration range, measurement wavelength, regression equations, and correlation coefficients for regression analysis. The precision evaluation data for the first-derivative spectrophotometric determination of BEMT-EHT and BEMT-DBT binary systems in this medium have been presented in Table 3. Both intra-day and inter-day precision studies demonstrate RSD below 2.86% (n=3), thereby confirming the high precision and reproducibility of the proposed first-derivative method.

Table 3. Quantitative parameters for the Binary mixture in DMSO/H2O (4:96, v/v) by the first-order derivative absorption spectra method, and precision data of BEMT-EHT and BEMT-DBT.
Binary mixture UV absorber Linearity range (mg L-1) λ (nm) Regression equation R2 Inter-dayb
Intra-dayc
Mean %RSD Day 1(n>=3) Day 2(n>=3) Day 3(n>=3) %RSD
BEMT-EHTa BEMT 1.0-11.0 390 dA/dλ=-0.00110 C + 0.0001 0.999 4.96 2.86 5.10 4.97 4.82 2.02
EHT 1.0-11.0 332 dA/dλ=-0.0036 C + 0.0001 0.997 6.98 0.73 6.97 7.03 6.93 2.18
BEMT-DBTa BEMT 1.0-11.0 384 dA/dλ=-0.00112 C - 0.0001 0.997 4.96 2.01 4.87 4.97 5.07 2.32
DBT 1.0-11.0 332 dA/dλ=-0.00389 C - 0.0001 0.995 7 1.72 7.1 7.03 6.87 2.51

aTheoretical concentration: 5 mg L-1 for BEMT and for 7 mg L-1 EHT., Theoretical concentration: 5 mg L-1 for BEMT and 7 mg L-1 for DBT.

bMean of determinations on 3 different days

cMean of 3 determinations

LODs for BEMT and EHT in the BEMT-EHT binary system were 0.52 and 0.35 mg L-1, respectively, while the LOQs were determined to be 1.58 and 1.06 mg L-1, respectively. LODs for BEMT and DBT in the BEMT-EHT binary system were 0.54 and 0.25 mg L-1L, respectively, while the LOQs were determined to be 1.64 and 0.76 mg L-1, respectively (Table S4). These values show that the proposed method has good sensitivity.

The accuracy assessment data for the BEMT-EHT and BEMT-DBT binary systems have been presented in Table 4. The results indicate mean recoveries of 97.85% for BEMT and 100.98% for EHT within the BEMT-EHT system, accompanied by corresponding mean relative errors of 2.15% and 0.98%. For the BEMT-DBT system, mean recoveries were found to be 99.00% for BEMT and 100.69% for DBT, with mean relative errors of 0.90% and 0.69%. The close agreement between nominal and experimentally determined values substantiates the accuracy of the proposed method.

Table 4. The recovery data for simultaneous determination of BEMT-EHT and BEMT-DBT by the first-order derivative UV spectrophotometric method in DMSO/H2O (4:96, v/v).
BEMT-EHT
BEMT-DBT
Theoretical (mg/L)
Experimental (mg L-1)
Recovery (%)
Error (%)
Theoretical (mg L-1)
Experimental (mg L-1)
Recovery (%)
Error (%)
BEMT EHT BEMT EHT BEMT EHT BEMT EHT BEMT DBT BEMT DBT BEMT DBT BEMT DBT
2.00 2.00 1.94 1.94 97.00 97.00 -3.00 -3.00 2.00 2.00 1.95 2.05 97.50 102.50 -2.50 2.50
4.00 4.00 3.85 4.07 96.25 101.75 -3.75 1.75 4.00 4.00 4.06 4.09 101.50 102.25 1.50 2.25
6.00 6.00 5.78 5.92 96.33 98.67 -3.67 -1.33 6.00 6.00 5.85 5.94 97.50 101.54 -2.50 1.54
8.00 8.00 7.94 8.07 99.25 100.88 -0.75 0.88 8.00 8.00 8.16 7.89 102.00 96.69 2.00 -3.31
5.00 3.00 4.84 3.05 96.80 101.67 -3.20 1.67 5.00 3.00 5.07 2.85 101.40 95.00 1.40 -5.00
3.00 5.00 3.07 5.08 102.33 101.60 2.33 1.60 3.00 5.00 2.95 5.06 98.33 101.20 -1.67 1.20
7.00 11.00 7.10 10.94 101.43 99.45 1.43 -0.55 7.00 11.00 6.88 11.12 98.29 101.09 -1.71 1.09
Mean±SD BEMT=98.49±2.54 EHT=100.14±1.83 Mean±SD BEMT=99.49±2.03 DBT=100.04±2.95

In addition, the robustness of the above two methods (as shown in Table S5) indicates that the analytical results are unaffected by minor variations in key experimental parameters, including scanning step size (Δλ), scanning speed, and temperature, thereby confirming the method’s reliability under typical operational conditions. The stability of the method was confirmed by monitoring changes in the recovery rate of three UV absorbers-BEMT, EHT, and DBT in a binary mixture across different solvents at 25±2°C over various time intervals (0, 12, 24, and 36 h), as presented in Table S6. These supplementary experiments and data enhance the method’s credibility and practical value.

Table S5

Table S6

4. Conclusions

In summary, this study successfully developed and validated a novel approach for the simultaneous quantitative analysis of multi-component triazine-based UV absorbers utilizing first-order derivative spectroscopy. This method effectively resolved critical spectral overlaps (e.g., BEMT-EHT, BEMT-DBT) across various solvent systems, including medium-polarity solvents (ethyl acetate, chloroform, dioctyl carbonate), polar solvents (DMSO, isopropanol, THF, 1,4-dioxane, acetonitrile, DMF), and mixed systems (DMSO/H₂O, isopropanol/H₂O), thereby enabling precise quantification. In contrast, solvents such as ethyl ether and MTBE exhibited poor peak morphology that compromised reliability. The method was validated in dioctyl carbonate and DMSO/water for rapid quality control and environmental water screening. It demonstrated excellent performance with high accuracy (95-103% recovery), good precision (RSD <2.5%), along with low limits of detection (LOD: 0.22-0.54 mg L-1) and quantitation (LOQ: 0.67-1.64 mg L-1). In comparison with HPLC, this approach is significantly faster, simpler, and more economical. It also provides a practical solution for labs requiring efficient analysis of multi-component UV absorber mixtures. Given the space constraints of this article, methodological parameter validation was not performed for all the other solvent systems, which represents a vital area for future research.

Acknowledgment

This work was supported by the Innovative Team Program of Natural Science Foundation of Hubei Province (2023AFA027), MFCI (Huangang) Co., Ltd., and the Department of Science and Technology of Hubei Province (No. 2025CSA001).

CRediT authorship contribution statement

Rong Chen: Writing – review & editing, Funding acquisition. Jianjun Liu: Methodology. Cheng Zeng: Data curation. Zhigang Wang: Conceptualization. Hong Gao: Writing – review & editing. Rundong Chen: Writing – original draft, Methodology, Data curation. Junji Chen: Writing – original draft, Methodology, Investigation, Data curation.

Declaration of competing interest

The authors declare no conflicts of interest.

Declaration of generative AI and AI-assisted technologies in the writing process

The authors confirm that there was no use of artificial intelligence (AI)-assisted technology for assisting in the writing or editing of the manuscript and no images were manipulated using AI.

Supplementary data

Supplementary material to this article can be found online at https://dx.doi.org/10.25259/AJC_855_2025.

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