Journal of Analytical Methods in Chemistry
Volume 2019 (2019), Article ID 3201370, 9 pages
https://doi.org/10.1155/2019/3201370

Research Article

Quantitative Characteristics of Toxic Compounds According to the Solvent Type

Young-Ji An,¹ Seong-Jin Choi,² Yong-Hyun Kim,2,3 and Kyuhong Lee3,4

¹Department of Toxicology Evaluation, Konyang University, Daejeon, Republic of Korea
²Jeonbuk Department of Inhalation Research, Korea Institute of Toxicology, Jeongeup 56212, Republic of Korea
³Human and Environmental Toxicology, University of Science and Technology, Daejeon 34113, Republic of Korea
⁴National Center for Efficacy Evaluation of Respiratory Disease Product, Korea Institute of Toxicology, Jeongeup 56212, Republic of Korea

Correspondence should be addressed to Yong-Hyun Kim; yonghyun.kim@kitox.re.kr and Kyuhong Lee; khlee@kitox.re.kr

Received 30 September 2018; Accepted 24 March 2019; Published 30 April 2019

Academic Editor: Paolo Montuori

Copyright © 2019 Young-Ji An et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract.

The quantitative analysis of target substances is an important part of assessing the toxicity of diverse materials. Usually, the quantitation of target compounds is conducted by instrumental analysis such as chromatography and capillary electrophoresis. If solvents are used in the pretreatment step of the target analyte quantification, it would be crucial to examine the solvent effect on the quantitative analysis. Therefore, in this study, we assessed the solvent effects using four different solvents (methanol, hexane, phosphate buffered saline (PBS), and dimethyl sulfoxide (DMSO)) and three toxic compounds (benzene, toluene, and methylisothiazolinone (MIT)). Liquid working standards containing the toxic compounds were prepared by dilution with each solvent and analyzed by gas chromatography-mass spectrometry (GC-MS). As a result, we found that the response factor (RF) values of the target analytes were different, depending on the solvent types. In particular, benzene and toluene exhibited their highest RF values (33,674 ng⁻¹ and 78,604 ng⁻¹, respectively) in hexane, while the RF value of MIT was the highest (9,067 ng⁻¹) in PBS. Considering the correlation (R²) and relative standard deviation (RSD) values, all target analytes showed fairly good values (R² > 0.99 and RSD < 10%) in methanol and DMSO. In contrast, low R² (0.0562) and high RSD (10.6%) values of MIT were detected in hexane, while benzene and toluene exhibited relatively low R² and high RSD values in PBS (mean R² = 0.9892 ± 0.0146 and mean RSD = 13.3 ± 4.1%). Based on these findings, we concluded that the results and reliability of the quantitative analysis change depending on the analyte and solvent types. Therefore, in order to accurately assess the toxicity of target compounds, reliable analytical data should be obtained, preferentially by considering the solvent types.

1. Introduction

Chemical products that are generally used to clean, sanitize, and disinfect are widely employed in our living environments. However, several of these are known to contain toxic compounds, which can damage the human health and natural environment [1, 2]. Due to their hazardous properties, these chemicals are usually regulated through a toxicology analysis such as safety assessment and toxicity testing [3]. In the toxicity testing, the accurate exposure of target chemicals to experimental animals or cells is important. As such, the stability of target chemicals should first be evaluated and ensured, the latter of which is commonly performed with the use of solvents [4, 5]. In case of the U.S. Environmental Protection Agency, the use of acetone, dimethylformamide (DMF), dimethyl sulfoxide (DMSO), and methanol as solvents is recommended for toxicity tests on aquatic invertebrates [6].

In general, a variety of solvents have been used to performing toxicity test [7, 8]. For example, in the case of an inhalation toxicity testing, solvents are mainly used for the sample extraction, absorption, and dilution steps. More specifically, if the filter sampling is conducted, the inhalable samples are first collected by filters (i.e., glass, quartz, or Teflon filters), after which the samples loaded on the filters are extracted and diluted by solvents [9–12]. Solvents are also used as the absorption solution to collect directly the inhalable samples [13]. In contrast, in the case of a cytotoxicity test, solvents are used for the storage and extraction of target analytes from cells [14, 15]. For this purpose, phosphate buffered saline (PBS) has been recommended as a suitable buffer solution to maintain the appropriate pH for cell storage [16, 17]. In addition, DMSO can be used as a sample extractant and cryoprotectant of cultured cells in biochemistry and cell biology [18].

Reportedly, the calibration results of target compounds can differ depending on the solvent effect due to the use of liquid samples [19, 20]. For example, Campos et al. [21] examined the reaction of an imidazole derivative with organic solvents by analyzing the imidazole samples derivatized from diethyl 2,4-dinitrophenyl phosphate and DMSO or distilled water as a solvent. As a result, they found that the imidazole derivative reaction increases in DMSO and decreases in distilled water, which indicates that the reactivity of derivation is different depending on the solvent type and that the reliability results can affect the quantitative analysis.

In this study, we investigated the solvent effect of toxic compounds in relation to their calibration characteristics. Methanol (MeOH), hexane, PBS, and DMSO, which are commonly used in the chemical and biological analysis, were selected as target solvents, while benzene, toluene, and methylisothiazolinone (MIT) were selected as target analytes (Table 1). From these, benzene and toluene are generally identified as carcinogenic, as they have the potential to damage the generative functions in humans upon transmission [22], whereas MIT is commonly known as the main component in humidifier disinfectants. The standard solutions containing the target analytes and solvents were analyzed using a gas chromatography (GC) equipped with a mass spectrometry (MS), which provided the calibration data to assess the solvent effects.

Table 1: Basic information on target compounds and solvents.

Chemical group
Full name
Short name
Molecular formula
Molecular weight (g·mol⁻¹)
Density (g·mL⁻¹)
m/za
CAS number
Chemical structure

Target compound
Benzene
—
C₆H₆
78.11
0.874
78
71-43-2

Toluene
—
C₆H₅CH₃
92.141
0.867
91
50643-04-4

Methylisothiazolinone
MIT
C₄H₅NOS
115.1
1.35
115
2682-20-4

Solvent compound
Methanol
MeOH
CH₃OH
32.04
0.792
31
67-56-1

Hexane
—
C₆H₁₄
86.18
0.6606
57
110-54-3

Phosphate buffered saline
PBS
Cl₂H₃K₂Na₃O₈P₂
411.029
0.0648
NA
NA

Dimethyl sulfoxide
DMSO
C₂H₆OS
78.13
1.1004
45,63,78
67-68-5

aMain spectra of the target compounds. NA, not available.

2. Materials and Methods

2.1. Preparation of the Working Standards (WSs)

A total of three target compounds (benzene, toluene, and MIT) and four solvents (MeOH, hexane, PBS, and DMSO) were selected to investigate the solvent effect. WSs of these three target compounds were prepared in the same way using each solvent. Reagent grade chemicals (RGCs) were purchased at ≥95% purity: (1) 99.5% (benzene and toluene), (2) 95% (MIT), and (3) 99.9% (MeOH, hexane, and DMSO) (Sigma-Aldrich, USA). PBS (1x, pH 7.4, Gibco BRL) was purchased from Life Technologies (Frederick, MD, USA). Primary standards (PSs) were prepared (PS-1 and PS-2) by mixing the RGCs with benzene and toluene or with MIT, respectively, with concentrations of 8,736 ng·μL⁻¹ (benzene), 8,627 ng·μL⁻¹ (toluene), and 90,000 ng·μL⁻¹ (MIT). The first working standards (1st-WSs) were prepared by mixing 100 μL of PS-1 and PS-2 each and 1800 μL of the respective solvent in a 2 mL vial, resulting in final concentrations (ng·μL⁻¹) of 416 (benzene), 411 (toluene), and 4,286 (MIT). Four different solvents were used to form the 1st-WSs: MeOH (1st-WS-M), hexane (1st-WS-H), PBS (1st-WS-P), and DMSO (1st-WS-D). The final working standards (F-WS-M, F-WS-H, F-WS-P, and F-WS-D) for the five-point calibrations were prepared by diluting each 1st-WS with the respective solvent to prepare five different concentrations: (1) benzene: 8.32, 20.8, 41.6, 83.2, and 208 ng·μL⁻¹, (2) toluene: 8.22, 20.5, 41.1, 82.2, and 205 ng·μL⁻¹, and (3) MIT: 85.7, 214, 429, 857, and 2,143 ng·μL⁻¹ (Figure 1(a)). Detailed information on the preparation of the WSs is shown in Table 2.

(a)

(b)

Figure 1: A plot of the experimental sequence for the preparation and analysis of the working standards (WSs). (a) Preparation of working standards. (b) Analysis of the working standards.

Table 2: Preparation of working standards (WSs) containing three target compounds (benzene, toluene, and MIT) based on four different solvents (MeOH, DMSO, hexane, and PBS).

(a) Reagent grade chemical (RGC)

Compound name
Benzene
Toluene
MIT

Concentration (%)
99.5
99.5
95

Density (g·mL⁻¹)
0.878
0.867
1.35

(b-1) The first primary standard (PS-1)

Compound
Benzene
Toluene
MeOH

Volume (μL)
20
20
1,960

Dilution fraction
0.010
0.010

Concentration (ng·μL⁻¹)
8,736
8,627

(b-2) The second primary standard (PS-2)

Compound
MIT

Mass (mg)
180

Volume (mL)
2.000

Concentration (ng·μL⁻¹)
90,000

(c) The first working standard (WS)

Working standard
PS-1
PS-2
Solventa

Compound
Benzene
Toluene
MIT

Volume (μL)
100
100
1,800

Dilution fraction
0.05
0.05

Concentration (ng·μL⁻¹)
416
411
4,286

(d) The final working standard at 5 concentration levels

Order
Mixing volume (μL)
Dilution fraction
Concentration (ng·μL⁻¹)

1st L-WS
Solvent
Benzene
Toluene
MIT

1
40
1,960
0.020
8.32
8.22
85.7

2
100
1,900
0.050
20.8
20.5
214

3
200
1,800
0.100
41.6
41.1
429

4
400
1,600
0.20
83.2
82.2
857

5
1,000
1,000
0.50
208
205
2,143

aFour solvents were used in this study: (1) MeOH, (2) DMSO, (3) hexane, and (4) PBS.

2.2. Instrumental System

A GC (GC-2010, Shimadzu, Japan) equipped with an MS (GCMS-QP2010 ultra, Shimadzu, Japan) was employed to quantify the toxic compounds in the solvents (Figure 1(b)). Since the F-WSs contained different solvents, the calibration characteristics of the toxic compounds according to the solvent effects were assessed.

In the analysis, 1 µL samples from the F-WSs were injected into the GC injector (at 250°C) using the autosampler (AOC-5000, Shimadzu, Japan). The target analytes were then transferred to the Rtx-5MS column (diameter: 0.25 mm, length: 60 m, and thickness: 0.25 µm, Restek Corporation, USA) for separation using a carrier gas (He > 99.999%, flow rate of 2.41 mL·min⁻¹ (constant flow)). The oven temperature of the GC was initially set to 40°C for 4 min, after which it was ramped at 15°C·min⁻¹ to 145°C, and finally ramped at 70°C·min⁻¹ to 285°C, thereby giving a total run time of 13 min.

The target analytes separated by the GC system were then detected by the MS system. Both the interface and ion source temperatures were set to 250°C. The target analytes were quantified in a total ion chromatogram (TIC) mode in a mass range of 30–500 m/z. Extracted ion chromatographic (EIC) mode was subsequently applied to the minimized interfaces using significant ions identified from the spectrum of each target analyte (Table 1). Detailed setting information of the analysis instrument is presented in Table 3.

Table 3: Instrumental setup for the analysis of target compounds (B, T, and MIT).

(a) Carrier gas settings

Injection temperature
250
°C

Injection mode
Split

Carrier gas
Helium (>99.999%)

Pressure
132.9
kPa

Column flow
2.41
mL·min⁻¹ (constant flow)

Purge flow
3.0
mL·min⁻¹

Split ratio
20

(b) Gas chromatography (model: GC-2010, Shimadzu, Japan)

Column
Rtx-5MS (Shimadzu, Japan)
(length: 60 m, diameter: 0.25 nm, and film thickness: 0.25 μm)

Oven setting
40°C (4 min) ⟶ 145°C (15°C/min) ⟶ 285°C (70°C/min)
(Total program time = 13 min)

(c) Mass spectrometry (model: GCMS-QP2010 ultra, Shimadzu, Japan)

Ionization mode
EI (70 eV)

Ion source temperature
250
°C

Interface temperature
250
°C

TIC
30∼500
m/z

Scan speed
1000

3. Result and Discussion

3.1. Calibration Characteristics of the Toxic Compounds According to the Solvent Type

The calibration results of the target analytes obtained by GC-MS analysis were provided in terms of the response factor (RF, ng⁻¹), coefficient of determination (R²), relative standard error (RSD, %), and limit of detection (LOD, ng) (Table 4).

Table 4: Experimental results for three target compounds (benzene, toluene, and MIT) based on four different solvents (MeOH, hexane, PBS, and DMSO), including the response factor (RF, ng⁻¹), normalized-RF (N-RF, ng⁻¹/ng⁻¹), determination of correlation (R²), relative standard deviation (RSD, %), and limit of detection (LOD, ng).

Solvent
Factors
Target compound

Benzene
Toluene
MIT

MeOH
RF (ng⁻¹)
26,164
43,618
7,877

N-RFa (ng⁻¹/ng⁻¹)
0.79
0.55
0.87

R²
0.9978
0.9984
0.9994

RSD (%)
0.83
0.72
5.56

LOD (ng)
0.02
0.01
0.07

Hexane
RF (ng⁻¹)
33,674
78,604
1,117

N-RF (ng⁻¹/ng⁻¹)
1
1
0.12

R²
0.9630
0.9969
0.0562

RSD (%)
4.22
2.35
10.6

LOD (ng)
0.01
0.00
0.18

PBS
RF (ng⁻¹)
11,286
21,026
9,067

N-RF (ng⁻¹/ng⁻¹)
0.34
0.27
1

R²
0.9788
0.9801
0.9997

RSD (%)
16.2
14.6
2.41

LOD (ng)
0.01
0.01
0.01

DMSO
RF (ng⁻¹)
31,932
60,147
8,148

N-RF (ng⁻¹/ng⁻¹)
0.95
0.77
0.90

R²
0.9984
0.9995
0.9998

RSD (%)
7.69
10.4
6.19

LOD (ng)
0.02
0.01
0.08

aNormalized-RF (N-RF): RF value/maximum RF among four different solvents.

Notably, the RF value of each target analyte was different, depending on the solvent type. The obtained RF values were normalized against the highest RF value in the following way: normalized-RF (N-RF) = RF/RF(max) (Table 4). Benzene and toluene had relatively high N-RF values (above 0.77) in hexane and DMSO, while in PBS (highly polar solvent), their N-RF values were significantly lower (0.34 and 0.27, respectively). In contrast, MIT exhibited the highest N-RF value in PBS (N-RF = 1), whereas in hexane, the N-RF value of MIT was low (N-RF = 0.12).

The calibration results derived in terms of R² and RSD (%) were similar to the patterns observed in the RF values (Figure 2). In particular, the R² values of benzene, toluene, and MIT in MeOH and DMSO were fairly high (>0.99). In MeOH, the RSD values of all target compounds exhibited the best reproducibility (below 6% for all target analytes), while in DMSO, the RSD values were slightly higher (mean RSD () = 8.09 ± 2.13%). When PBS and hexane were used as solvents, the R² and RSD values of the target compounds differed upon changing the solvent types. In hexane, the R² values of benzene and toluene exhibited a strong linearity (>0.96), while that of MIT was low (0.0562). Also, benzene and toluene showed good RSD values in hexane (<5%), whereas MIT had a high RSD (10.6%). In contrast, the RSD and R² values when PBS was used as a solvent were contrary to those obtained in the case of hexane. In particular, the R² and RSD values of MIT in PBS were 0.9997 and 2.41%, respectively, while the RSD values of benzene and toluene showed low reproducibility with above 14%. The LOD values of all target analytes were below 0.18 ng, which is sufficient to detect the lowest calibration points of all the types of final working standards (F-WSs) (Table 4).

(a)

(b)

(c)

(d)

Figure 2: Chromatograms of the three target compounds based on four different solvents. The concentrations varied 208 ng·μL⁻¹ (benzene), 205 ng·μL⁻¹ (toluene), and 2,143 ng·μL⁻¹ (MIT). (a) MeOH solvent. (b) DMSO solvent. (c) Hexane solvent. (d) PBS solvent.

Based on these results, we concluded that the instrument responsivity and reproducibility of the target compounds differed, depending on their physicochemical properties. Moreover, the responsivity and analytical reliability was found to be especially affected by the solvent type. Therefore, in order to achieve an accurate quantitation, it is important to select the solvent by considering the physicochemical properties (i.e., polarity) of the target analytes.

3.2. Comparison of Previous Research Data

Diverse solvents have been previously used in chemical and biological analyses for the pretreatment of target samples and the preparation of standard solutions. In this study, we confirmed that the calibration results were different depending on the solvent type, although the same target compounds were analyzed by the same analytical methods. However, many researchers do not fully consider the solvent effect in their quantitative analyses (Table 5).

Table 5: List of the comparison of the solvent effects on chemical and biological analysis using the analytical instrument.

Order
Field of science
Target compound or material
Pretreatment or standard solvent
Sample solvent
Instrument or assay methoda
Reference

1
Chemistry
13 aldehydes and 4 ketones
Water and acetonitrile
Water and methanol
HPLC-UV
Brandão et al. [23]

2
Formaldehyde in bovine milk
Ultrapure water
Acetonitrile
HPLC-UV
Rezende et al. [24]

3
Sodium ferrocyanide in 801 Salt
0.02 M NaOH
0.02 M NaOH
HPLC-UV
Lim et al. [25]

4
Biology
Ginkgo biloba L. (EGB)
Methanol
Isopropanol-ethanol-water (3 : 2 : 1)
HPLC-UV/DAD/MS
Yang et al. [26]

5
Vitamin C (ascorbic acid and dehydroascorbic acid)
10% meta-phosphoric acid
10% meta-phosphoric acid
HPLC or UPLC
Klimczak & Gliszczyńska-Świgło [27]

6
Sugars content in sunflower oil
0.005 N H₂SO₄
Ethanol and distilled water
HPLC
Baumler et al. [28]

7
37 raw vegetables
Acetone, methanol, ethanol, and distilled water
2,2-Diphenyl-1-picrylhydrazyl (DPPH) in ethanol
DPPH free radical scavenging assay
Sulaiman et al. [29]

Distilled water
Total phenolic content

aHPLC, high-performance liquid chromatography; UV, ultraviolet/visible; DVD, diode array detection; UPLC, ultraperformance liquid chromatography.

For example, Rezende et al. [24] analyzed formaldehyde in bovine milk using high-performance liquid chromatography-ultraviolet/visible (HPLC-UV) by employing ultrapure water as a standard solvent and acetonitrile as a sample solvent. Moreover, Baümler et al. [28] analyzed sugars in sunflower oil samples using HPLC by extracting them with ethanol and subsequently diluting the samples with distilled water. Additionally, a 0.005 N H₂SO₄ solution was used as a standard solvent. In both of these cases, there could be a quantitative error due to the solvent difference between the standards and samples.

Furthermore, there are also studies that use the same solvent for both standard and sample preparation. For instance, Lim et al. [25] analyzed ferrocyanide ions using HPLC-UV by employing the same solvent (0.02 M NaOH solution) for the preparation of the standard solution and pretreatment of the sample. In addition, Klimczak and Gliszczyńska-Świgło [27] quantified vitamin C (ascorbic acid and dehydroascorbic acid) using HPLC and ultraperformance liquid chromatography (UPLC) systems by using 10% meta-phosphoric acid solvent to both extract the samples and dilute the standard solutions. In both of these cases, the solvent effects could be minimized by using the same solvent for the quantitative analysis.

4. Conclusion

In order to conduct a toxicity testing, one needs to be able to obtain reliable quantitation data of the target toxic compounds. In this study, we assessed the effect of the solvent type on the quantitative results by analyzing three toxic compounds using four different solvents. Benzene, toluene, and MIT, which are well-known toxic compounds, were selected as target analytes. Liquid working standards of the target analytes were prepared using four different solvents (MeOH, hexane, PBS, and DMSO), which are commonly used for extraction and dilution of sample solutions. These working standards were analyzed using GC-MS, thereby providing the calibration results of the target compounds according to the solvent type. The solvent effect was then assessed by comparing these results (Figure 3). The RF values of nonpolar compounds (benzene and toluene) were the highest (33,674 ng⁻¹ (benzene) and 78,604 ng⁻¹ (toluene)) in nonpolar solvents such as hexane and the lowest (11,286 ng⁻¹ (benzene) and 21,026 ng⁻¹ (toluene)) in the polar solvent such as PBS. Unlike benzene and toluene, MIT had the highest RF value (9,067 ng⁻¹) in a polar solvent (PBS), while it dropped dramatically to 1,117 ng⁻¹ in a nonpolar solvent (hexane). Additionally, in MeOH, all target compounds showed fairly good reproducibilities with RSDs below 6% and linearity above 0.99. In contrast, hexane induced a low R² value of MIT (0.0562), and PBS led to high RSD values of benzene and toluene (above 14%).

(a)

(b)

(c)

(d)

(e)

Figure 3: Plots of the calibration results from the three target compounds (B, T, and MIT) according to the four different solvents. (a) Response factor. (b) Normalized-RF. (c) Determination of correlation. (d) Relative standard deviation. (e) Limit of detection.

All in all, the results of this study confirmed that the quantitative results were affected by the solvent effect. Since quantitative results can differ depending on the solvent type, it is important to select the solvent by considering the physicochemical properties (i.e., polarity) of the target compounds. In addition, the use of different solvents in the quantitative analysis, such as in the extraction and dilution processes, could lead to difficulties in obtaining reliable quantitative data.

Data Availability

The data used to support the findings of this study are included within the article.

Conflicts of Interest

The authors declare that they have no conflicts of interest.

Acknowledgments

This work was supported by the Korea Institute of Toxicology, Republic of Korea (KK-1803 and KK-1904).

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