Skip to main content
Iranian Journal of Pharmaceutical Research : IJPR logoLink to Iranian Journal of Pharmaceutical Research : IJPR
. 2020 Summer;19(3):183–194. doi: 10.22037/ijpr.2019.15323.13018

Development of a GC-MS Method for Determination of Various Polycyclic Aromatic Hydrocarbons in Iranian Traditional and Semi-industrial Taftoon Bread

Vahideh Moradi a, Seyed Mahdi Seyedain Ardabili a, Attaollah Shakoori b,*, Seyed Ebrahim Hoseyni a
PMCID: PMC7757998  PMID: 33680021

Abstract

This research reports a validated multi-residue method based on gas chromatography coupled mass spectrometry technique for analysis of 24 Polycyclic Aromatic Hydrocarbons (PAHs) in traditional and semi-industrial Taftoon bread using QuEChERS sample preparation.

Matrix effect studies were performed by comparing the slopes of solvent based standard calibration curves and spiked calibration curves. Due to enhancement or suppression effects of matrix, validation of the method was performed using spiked calibration curves. In the concentration range of 10-500 ng/g, the calibration curves for each analyte was linear with a determination coefficient (R2) of 0.991-0.999. The Detection and quantitation limits for the studied PAHs were calculated 0.14-1.49 ng/g and 0.46-4.91 ng/g. The average recoveries for three spiked levels (25, 50 and 200 ng/g), were in the range 77-103% (n = 27), with a satisfactory precision (RSD < 20%).

Analysis of Taftoon bread samples using the validated method showed that three compounds; NPH, PHE and ANT were found in 37 (35.2%) samples and in the term of traditional and semi- industrial samples the occurrence of mentioned PAHs were 36.1% and 33.3%, respectively. According to the findings, we proposed that direct flame exposure in gas oven during baking of Taftoon bread could produce PAHs in bread samples.

Key Words: GC-MS, Polycyclic Aromatic Hydrocarbons (PAHs), Taftoon bread, Iran

Introduction

Polycyclic aromatic hydrocarbons (PAHs) are a large class of highly lipophilic compounds containing fused aromatic ring. Chemically, they can be divided into light (2-4 rings) and heavy (5 or more rings) groups on the basis of the number of condensed aromatic rings. It has been known that the heavy PAHs, such as benzo[a] pyrene, dibenzo[a,h] anthracene, benzo [g,h,i] perylene, and indeno [1,2,3-c,d] pyrene are more stable and more toxic than the light ones (1, 2). Numerous organizations for example the International Agency for Research on Cancer (3), the European Food Safety Authority (4) and the others consider PAHs to be toxic compounds with carcinogenic, teratogenic, and mutagenic properties.

According to the studies on PAHs exposure, food is the main source of human exposure to PAHs. Food contaminated with PAHs generally arises from environmental contamination (including Polluted water and soil, agricultural burning and Post-harvest), food processing, contaminated packaging, and direct contact with non-food grade mineral oil (5-10).

As shown, PAHs can occur in various foods and cereals are one of the major sources (10-12). Wheat, as an important cereal is produced in the worldwide and widely consumed in different forms, including bread. Bread is prepared from wheat-flour dough then cultured with yeast, and finally baked in various methods such as oven.

Some international investigations have shown that PAHs can be occurred in bread in different ways, both through the environmental pollutants and during baking processes (10-17). Because of daily and high per capita consumption, occurrence of PAHs in bread can cause a major concern for human health.

Nowadays, various methods have been established for Analysis of PAHs in food matrixes based on chromatographic detections. Numerous extraction methods have been introduced to removal of PAHs in foods, like the lipid extraction methods, followed by various preparation techniques (7). Instrumentally, the most commonly reported technique for analysis of PAHs is gas chromatography (GC) coupled different detectors. GC coupled mass spectrometry (MS) detector owing to high selectivity and sensitivity is a powerful instrument for detection and trace analysis of PAHs in foods and other commodities. Molecularly, PAHs are very stable compounds, and in the ionization process, they are mainly fragmented to the molecular ion ([M-H]‏ or [M-2H]). Thus, the single MS (quadrupole) are appropriate technique for analysis of PAHs in food samples (7, 12 and 18). Few studies reported the use of GC- tandem mass spectrometry (GC-MS/MS) or GC- high-resolution mass spectroscopy (GC-HRMS) for analysis of PAHs in various matrixes (19, 20).

Bread is one of the most valuable foodstuffs around the world (21). It is the main food of the Iranian people, and cooked by using traditional and industrial methods. Traditional Iranian breads are very popular and renowned for their taste. Because of ethnic and racial variety, many types of traditional breads are baked in different regions of Iran such as, Taftoon, Lavash, Barbari, and Sangak. Taftoon is categorized as flat circle bread and produced by mixing wheat flour, water, salt, and leaven. Previously, Taftoon was baked in a clay oven, but in recent decades it is mainly prepared in direct gas fired machines (22).

In Iran, a few investigations have been conducted on occurrence of PAHs in breads especially traditional breads. Recently, Eslamizad et al. developed a modified QuEChERS extraction for detection and determination of benzo[a]pyrene (BaP), the well-known member of PAHs, in traditional, semi-industrial, and industrial Sangak bread samples (23). They detected different amounts of BaP in the collected samples. In this study, only BaP was investigated and other PAHs were not conducted. Due to great consumption of Taftoon in Iran, development a new mothed for assessment of BaP and other PAHs in Taftoon bread samples is required.

In this investigation, a reliable method was developed for analysis of 24 PAHs in traditional Taftoon bread using GC-MS then, the established method was used to detection of studied PAHs in Taftoon bread samples collected in various different of Tehran.

Experimental

Chemicals and reagents

A 15 mixed standards of PAHs including; benzo[c]fluorene (B[c]F,97%), benzo[a]anthracene (B[a]A,99%), chrysene (CHR, 99%), 5-metylchrysene (5-MChr,99%), cyclopenta[c,d]pyrene (C[cd]P,99%), benzo[b]fluoranthene (B[b]F,99%), benzo[k]fluoranthene (B[k]F,99%), benzo[a]pyrene (B[a]P,99%), dibenzo[a,h]anthracene (D[ah]A, 99%), indeno[1,2,3-cd]pyrene (I[cd]P, 99%), benzo[g,h,i]perylene (B[ghi]P, 99%), dibenzo[a,l]pyrene (D[al]P, 99%), dibenzo[a,e]pyrene (D[ae]P, 99%), dibenzo[a,i]pyrene (D[ai]P, 99%) and dibenzo[a,h]pyrene (D[ah]P, 99%) were provided from Restek company (United States) and 9 single chemicals including; Phenanthrene (PHE, 99.20%), Naphthalene (NPH, 99.40%), Fluorene (FLR, 99.90%), Fluoranthene (FLA, 98.7%), Pyrene (PYR, 98%), Anthracene (ANT, 99.40%), Acenaphthene (ACP, 99.9%), Perylene (PER, 99.9%), Acenaphtylene (ACL, 99.9%) were prepared from Sigma Aldrich (United states). Stock standards of 9 single PAHs were prepared at concentration 1000.0 μg/mL in Ethyl acetate then; a mixed solution of all PAHs standards was made ready by dissolving appropriate concentration of 15 mixed standards and 9 single standards in acetonitrile at a concentration of 5.0 μg/mL. Primary and working standards were prepared from the final mixed standard. All standard solutions were stored in amber flasks at -20 °C.

Triphenylphosphate (TPP), as internal standard was obtained from Sigma–Aldrich (Germany). A stock solution of TPP in ethyl acetate at concentration of 10.0 μg/mL was prepared and a 50.0 μL of its solutions was added to the spiked bread samples. Anhydrous magnesium sulfate (MgSO4) was acquired from Sigma–Aldrich (Germany) and Methanol (MeOH) and HPLC-grade acetonitrile (MeCN) from Acros (Belgium). Ethyl acetate (EtAc) and sodium acetate were supplied from Merck (Darmstadt, Germany). Bondesil-primary secondary amine (PSA, 40 μm) was provided from Interchim (France). A Milli-Q Plus ultra-pure water system (Molsheim, France) was applied for preparation of HPLC grade water.

Instrument Analysis

All samples were determined using an Agilent 7890A GC instrument coupled a 5975C mass detector with split/spiltless injector, and 7693 autosampler (Agilent technologies, USA). A DB-5MS 122-5532UI capillary column (30 m × 0.25 mm I.D., 0.25-μm film) from Agilent technologies and Helium carrier gas (purity 99.999%) at a constant flow rate of 1.6 mL/min with the following oven temperature program was applied: 80 °C (2 min), 20 °C/min ramp to 140 °C (1 min), then 5 °C/min ramp to 315 °C. Injection port, quadrupole mass analyser, transfer line and ion source was adjusted at 300 °C, 100 °C, 280 °C, and 230 °C, respectively and splitless mode was used. A mass range of m/z 50-500 was scanned to find the retention time and diagnostic ions (quantification and confirmation ions) of the analytes. After acquisition of the diagnostic ions in selected ion monitoring (SIM) mode, the retention times and mass spectra of selected ions were used to identification of peaks. At least three ions were used to recognition and determination of analytes. The most abundant ions with the highest signal-to-noise ratios were chosen as quantifiers and the others were qualifiers. All identified peaks were confirmed by comparing the relative abundances of studied ions of PAHs to the related spectra in the mass reference library.

Sample preparation

Sample preparation including, extraction and clean-up was performed according to the QuEChERS method (24). The bread samples were carefully ground and homogenized, then a 5 g portion of the obtained powder was transferred into a 50 mL falcon tube. The desired amounts of the mixed PAH standard (for spiking) and 50 µL TPP (200 ng/mL) were included to the tube. Thereafter, by adding 14 mL of MeCN, the studied PAHs were taken out bread. The tube content was vortex mixed for 3.0 min, then 2 g anhydrous MgSO4 and 1.5 g sodium acetate were added and after mixing for another 3.0 min the content was introduced to a centrifuge 9055×g for 20 min. After centrifugation, the 7 mL of supernatant was taken into a suitable tube and evaporated until dryness by a nitrogen evaporator. The remainder was reconstituted in 0.5 mL MeCN and sonicated 10.0 min then vortex mixed for 3.0 min. The obtained solution was transferred to a micro tube containing 60 mg anhydrous MgSO4 and 20 mg PSA and vortex mixed vigorously for 1min and centrifuged for 5 min 18894×g. Finally, a desired amount of aliquot was transferred into a screw cap vial and 2.0 μL was injected into GC-MS.

Method validation

For validation studies, various parameters including; linearity, recovery, precision, limits of detection (LOD) and limits of quantification (LOQ) were calculated (25-27). Linearity was assessed applying spiked calibrations by analyzing in triplicate six concentration levels, between 10 and 500 ng/g. To estimation of the accuracy (recovery studies) and the precision, three spiked blank bread samples at concentration levels of 25, 50, and 200 ng/g were prepared. The matrix effects were calculated as: [1 - (spiked calibration curve slope/solvent base calibration curve slope)] ×100 (24). LODs and LOQs were estimated according to the concentrations of PAH resulting in a signal-to-noise ratio of 3 and 10, respectively. The amounts of PAHs in Taftoon samples were calculated by interpolation of the peak areas for each PAH to internal standard peak area in the sample.

Determination of PAHs in Taftoon samples

Seventy-two traditional and thirty-three semi- industrial Taftoon bread samples collected from Taftoon bakeries located in Tehran city. Traditional bread were baked by direct heating in the temperature range of 216-300 °C and semi-industrial bread were baked by indirect heating at temperatures between 160 and 300 °C in different distance of heating source. Natural gas had been used for both of the oven. After collection, all of the samples were covered with aluminum foil and transported to the lab. Each sample was coded and dried to lose its moisture within one day. Then all of the samples were ground and stored in amber glass bottles at 20 °C until analysis. Finally, 50 g portion of homogenized samples was weighted and analyzed.

Results and Discussion

Gas chromatography mass spectrometry determination

Optimization of GC and MS conditions as a key point in the analysis was accurately conducted. Various GC parameters including oven temperature program, MS conditions, and assess to suitable column were obtained by consecutive injections. Therefore, the SIM mode was applied for analysis of the investigated PAHs. Quantitation and confirmation of PAHs were performed based on the use of: one target as quantification ion, at least two confirmations, their ion ratios and also retention times. Table 1 summarizes molecular weights, retention times, SIM conditions, and calculated ion ratios obtained for the studied PAHs. A chromatogram of some PAH standards (A), and detected PAHs (NPH, PHE and ANT) in Taftoon samples (B) are shown in Figure 1.

Table 1.

Molecular weights, quantification and confirmation ions, ion ratio and retention times of studied PAHs

NO. Compounds Molecular
Weights (g/mol)
Quantification Ions (m/z) Confirmation Ions (m/z) Ion Ratios Retention Times (min)
1 NPH 128 128 128 ,129*,64 8.393 5.19
2 ACL 152 152 152,151*,76 4.509 8.18
3 ACP 154 153 153,154*,76 3.231 8.63
4 FLR 166 166 166,165*,82 1.176 10.16
5 PHE 178 178 178,176*,152 5.13 12.91
6 ANT 178 178 178,176*,152 8.441 13.09
7 FLA 202 202 202, 203*,201 6.76 17.40
8 PYR 202 202 202, 203*,201 6.546 18.27
9 B(c)F 216 216 216, 215*,217 1.349 20.17
10 CP(c,d)P 226 226 226, 227*,225 8.634 23.49
11 B(a)A 228 228 228.226*,229 2.906 23.66
12 CHR 228 228 228.226*,229 3.456 23.79
13 5-M-CHR 242 242 242, 241*,239 2.158 25.82
14 B(b)F 252 252 252, 253*,250 5.106 28.25
15 B(k)F 252 252 252, 253*,250 3.431 28.35
16 B(a)P 252 252 252, 253*,250 6.624 29.76
17 PER 252 252 252, 253*,250 4.613 29.96
18 I(1,2,3-cd)P 276 276 276, 277*,138 5.071 33.45
19 DB(a,h)A 278 278 278, 276*,138 3.733 33.67
20 B(g,h,i)PER 276 276 276, 138*,277 20.08 34.25
21 DB(a,l)P 302 302 302, 303*,300 4.329 37.84
22 DB(a,e)P 302 302 302, 303*,300 4.784 38.84
23 DB(a,i)P 302 302 302, 303*,300 4.395 39.19
24 DB(a,h)P 302 302 302, 303*,300 3.151 39.37

*Selected confirmation ion.

Figure 1.

Figure 1

Chromatogram of some PAH standards; (A) TPP as the internal standard, NPH (1); FLR (2); PHE (3); ANT (4); FLA (5); B[c]F (6); 5-M-CHR (7); B[b]F (8); B[g,h,i]PER (9); DB[a,e]P (10). (B) Detected PAHs in aftoon bread samples

Validation studies

Validation studies were performed for assessment of linearity, accuracy, precision, and limits of detections (LOD) and quantifications (LOQ). One of the most important challenges in development of an analytical method is matrix effect. In this challenge, components of the sample affect the results of an analysis, altering assay sensitivity and repeatability (28). In food analyses by GC-MS, original components, such as peptides, sugars, and lipids or added ingredients contribute in matrix are effected by interfering gas chromatography and/or mass spectrometry (29). Components of Taftoon bread, like salt, wheat protein, and carbohydrates can lead to suppression or enhancement of targeted ions in mass spectrometry assay. Matrix effect was calculated by comparing the slopes of solvent based calibration curves and spiked calibration curves and declared in terms of ion suppression or enhancement. As shown in Table 2, matrix effect for all of the analytes shows a strong signal enhance (>50%) except matrix effect for BbF and BghiPER considered medium signal enhance whereas that was medium and strong suppression signal in BaA and DBahA, respectively. There are various solutions for overcoming of matrix effects, and in this study spiked calibration standard approach was used. Spiked calibration standards at levels of 10, 25, 50, 100, 200, and 500 ng/g were prepared by the addition of 10, 25, 50, 100, 200, and 500 μL of standard stock solutions with concentration of 5000 ng/mL to 5 g of blank bread samples in each case, respectively. Quantification of the PAH compounds in the bread samples was performed by using an internal standard method. Therefore 50 μL of TPP solution in acetonytril (20,000 ng/mL) was added to the all spiked bread samples.

Table 2.

Matrix effects of studied PAHs in spiked and solvent-based calibration curves

NO. Compound Spiked calibration curve of bread
Solvent calibration
curve
A Matrix Effect (%)
Slope R 2 Slope R 2
1 NPH 0.0002 0.989 0.009 0.998 0.022 97.78
2 ACL 0.002 0.998 0.023 0.997 0.098 90.15
3 ACP 0.002 0.998 0.026 0.991 0.088 91.19
4 FLR 0.005 0.997 0.020 0.999 0.249 75.12
5 PHE 0.005 0.998 0.010 0.994 0.490 50.94
6 ANT 0.003 0.998 0.008 0.999 0.410 58.98
7 FLA 0.007 0.999 0.018 0.994 0.379 62.13
8 PYR 0.007 0.996 0.041 0.992 0.175 82.47
9 B(c)F 0.006 0.999 0.059 0.999 0.103 89.72
10 CP(c,d)P 0.006 0.996 0.015 0.993 0.375 62.48
11 B(a)A 0.005 0.999 0.004 0.999 1.366 -36.64
12 CHR 0.006 0.999 0.013 0.998 0.423 57.65
13 5-M-CHR 0.005 0.999 0.014 0.995 0.352 64.80
14 B(b)F 0.008 0.999 0.012 0.999 0.705 29.52
15 B(k)F 0.003 0.999 0.009 0.999 0.341 65.91
16 B(a)P 0.006 0.992 0.016 0.995 0.393 60.71
17 PER 0.007 0.999 0.026 0.997 0.265 73.48
18 I(1,2,3-cd)P 0.006 0.998 0.014 0.993 0.422 57.79
19 DB(a,h)A 0.005 0.999 0.002 0.990 2.174 -117.38
20 B(g,h,i)PER 0.009 0.998 0.015 0.999 0.616 38.44
21 DB(a,l)P 0.004 0.998 0.014 0.997 0.271 72.93
22 DB(a,e)P 0.004 0.999 0.025 0.994 0.157 84.27
23 DB(a,i)P 0.003 0.996 0.025 0.994 0.127 87.33
24 DB(a,h)P 0.002 0.998 0.026 0.994 0.078 92.15

Calibration curves showed a linear relationship between the concentration and peak area ratios in the range of 10-500 ng/g with a determination coefficient (R2) ranging between 0.991 and 0.999. Therefore, the extraction processes and analytical method had enough efficiency for the determination of PAHs at trace levels. Table 3 shows the values of the validation parameters for analytes quantification of spiked calibration (range 10-500 ng/g of triplicates each, n = 18).

Table 3.

Regression equations and coefficients of determination (R2), LOQs, LODs (ng/g) obtained for studied PAH in bread samples

NO. Compound Regression Equation (n = 18) Coefficients of Determination (R 2 ) LOD a LOQ b
1 NPH y = 0.0003x + 0.009 0.99 1.49 4.91
2 ACL y = 0.002x + 0.038 0.998 0.65 2.50
3 ACP y = 0.025x + 0.134 0.991 0.65 2.15
4 FLR y = 0.005x + 0.052 0.997 0.75 2.48
5 PHE y = 0.005x + 0.077 0.998 0.61 2.01
6 ANT y = 0.003x + 0.011 0.998 0.56 1.85
7 FLA y = 0.006x - 0.006 0.999 0.14 0.46
8 PYR y = 0.007x - 0.037 0.996 0.87 2.88
9 B(c)F y = 0.006x - 0.002 0.999 0.18 0.60
10 CP(c,d)P y = 0.005x - 0.002 0.996 0.82 2.71
11 B(a)A y = 0.005x + 0.012 0.999 0.24 0.80
12 CHR y = 0.013x - 0.068 0.998 0.20 0.67
13 5-M-CHR y = 0.005x + 7E-05 0.999 0.24 0.80
14 B(b)F y = 0.008x + 0.015 0.999 0.35 1.15
15 B(k)F y = 0.003x + 0.008 0.999 0.39 1.28
16 B(a)P y = 0.017x - 0.106 0.994 0.79 2.59
17 PER y = 0.006x + 0.012 0.999 0.39 1.29
18 I(1,2,3-cd)P y = 0.006x + 0.021 0.998 0.56 1.85
19 DB(a,h)A y = 0.005x + 0.004 0.999 0.36 1.19
20 B(g,h,i)PER y = 0.009x + 0.072 0.998 0.58 1.90
21 DB(a,l)P y = 0.014x - 0.057 0.997 0.59 1.96
22 DB(a,e)P y = 0.004x + 0.011 0.999 0.30 1.52
23 DB(a,i)P y = 0.003x + 0.020 0.996 0.84 2.76
24 DB(a,h)P y = 0.002x + 0.027 0.998 0.57 1.88

aLOD: limit of detection for a S/N = 3.

bLOQ: limit of quantification for a S/N = 10.

Limits of detection (LODs) and Limits of quantification (LOQs) were calculated based on the signal-to-noise ratio of equal to 3 and 10, respectively. The LODs and LOQs as shown in table 3 were between 0.14-1.49 ng/g and 0.46-4.91 ng/g, respectively.

The mean extraction recoveries were determined by applying the full procedure to triplicate samples in three consecutive days of analysis at three spiking levels including 25, 50, and 200 ng/g with the same operator and laboratory. The percentage of mean recoveries obtained 77-103% for each PAH compound considered as the acceptable range of European Commissions regulation (26).

Precision was expressed as relative standard deviation (RSD) and calculated like the recovery in different days. The average of relative standard deviations (RSDs) of PAHs in bread were in the range of 3.52-17.26% with a satisfactory precision (RSD<20%) which were in the acceptable range of European Commissions regulation (26). The values of mean recovery and RSD percentage for each spiking level are presented in Table 4.

Table 4.

Recoveries (%) and relative standard deviations (RSD, %) obtained for studied PAHs in Taftoon bread samples, spiked at 25, 50 and 200 ng/g levels (n = 9).

NO. Compound 25 (ng/g)
50 (ng/g)
200 (ng/g)
Average recovery
(n = 27)
Average
RSD
(n = 27)
Recovery RSD Recovery RSD Recovery RSD
1 NPH 117.72 17.28 111.36 10.83 71.14 18.69 100.07 15.60
2 ACL 98.21 4.77 111.72 6.89 99.18 10.81 103.04 7.49
3 ACP 114.96 6.58 108.04 9.59 75.99 18.35 99.66 11.51
4 FLR 90.37 3.36 92.15 6.14 104.91 5.36 103.04 7.49
5 PHE 89.19 1.39 96.83 6.04 79.89 15.22 88.64 7.55
6 ANT 93.96 1.37 98.26 5.09 80.65 13.47 90.96 6.64
7 FLA 108.52 1.11 107.89 2.31 77.28 10.25 97.89 4.56
8 PYR 115.40 0.94 112.79 1.66 78.38 7.97 102.19 3.52
9 B(c)F 104.73 1.09 105.96 1.76 74.29 9.33 94.99 4.06
10 CP(c,d)P 92.13 1.76 85.25 2.16 64.17 7.38 80.52 3.77
11 B(a)A 86.75 3.58 94.43 2.01 81.26 20.11 87.48 8.57
12 CHR 100.15 1.67 99.95 1.89 72.09 10.20 90.73 4.59
13 5-M-CHR 100.69 1.62 103.70 1.96 73.47 10.67 92.62 4.75
14 B(b)F 93.35 1.93 104.36 2.74 73.24 9.18 90.31 4.62
15 B(k)F 90.31 2.44 98.06 2.56 74.08 13.40 87.49 6.13
16 B(a)P 90.28 3.09 94.18 4.40 67.10 8.70 83.85 5.40
17 PER 96.94 1.99 103.72 2.27 76.38 7.76 92.35 4.01
18 I(1,2,3-cd)P 82.10 1.63 88.71 5.90 61.90 14.53 77.57 7.35
19 DB(a,h)A 116.87 4.42 108.82 5.16 80.93 13.58 102.20 7.72
20 B(g,h,i)PER 91.46 1.71 101.39 3.92 69.57 7.33 87.48 4.32
21 DB(a,l)P 81.52 2.89 100.76 4.83 71.23 6.67 84.51 4.80
22 DB(a,e)P 101.24 4.07 116.09 4.32 73.38 8.36 96.90 5.58
23 DB(a,i)P 75.87 2.95 94.87 5.91 64.38 14.12 78.38 7.66
24 DB(a,h)P 101.42 6.42 108.69 7.43 75.86 37.94 95.33 17.26

Determination of PAHs in Taftoon samples

The developed method was successfully used for detection and determination of 24 PAHs in various traditional and semi- industrial Taftoon bread samples collected from different region of Tehran, the capital of Iran. Totally, 105 Taftoon samples including, 72 traditional, and 33 semi- industrial were analyzed (Tables 5 and 6). The results showed that three compounds; NPH, PHE, and ANT were found in 37 (35.2%) Taftoon samples and in the term of traditional and semi- industrial samples the occurrence of mentioned PAHs was 36.1% and 33.3%, respectively. As shown in table 5 and 6, NPH was found in 20 (27.8%) traditional Taftoon samples and in 7 (21.2%) semi- industrial samples in the range of 7.17-201.1 and 5.09-241.15 ng/g, respectively. ANT was detected in 5 (6.9%) traditional and in 3(9.1%) semi- industrial samples in the range of 9.82-18.09 and 10.73-11.12 ng/g, respectively. One sample (1.4%) of traditional and 1 sample (3.0%) semi- industrial Taftoon was found to be contaminated with PHE in levels 2.29 ng/g and 6.76, respectively. All obtained results were higher than the legal permissible limits (1.0 ng/g) proposed by the European Union for processed cereal-based foods (30).

Table 5.

PAHs values determined in traditional Taftoon bread samples (n = 72).

NO. Compound Numbers of positive samples LOD
(ng/g)
LOQ
(ng/g)
Mean
(ng/g)
Min Level
(ng/g)
Max Level
(ng/g)
1 NPH 20 (27.8%) 1.49 4.91 88.68 7.17 201.10
2 ACL 0 0.65 2.50 0 nd nd
3 ACP 0 0.65 2.15 0 nd nd
4 FLR 0 0.75 2.48 0 nd nd
5 PHE 1 (1.4%) 0.61 2.01 2.29 - 2.29
6 ANT 5 (6.9%) 0.56 1.85 12.33 9.82 18.09
7 FLA 0 0.14 0.46 0 nd nd
8 PYR 0 0.87 2.88 0 nd nd
9 B(c)F 0 0.18 0.60 0 nd nd
10 CP(c,d)P 0 0.82 2.71 0 nd nd
11 B(a)A 0 0.24 0.80 0 nd nd
12 CHR 0 0.20 0.67 0 nd nd
13 5-M-CHR 0 0.24 0.80 0 nd nd
14 B(b)F 0 0.35 1.15 0 nd nd
15 B(k)F 0 0.39 1.28 0 nd nd
16 B(a)P 0 0.79 2.59 0 nd nd
17 PER 0 0.39 1.29 0 nd nd
18 I(1,2,3-cd)P 0 0.56 1.85 0 nd nd
19 DB(a,h)A 0 0.36 1.19 0 nd nd
20 B(g,h,i)PER 0 0.58 1.90 0 nd nd
21 DB(a,l)P 0 0.59 1.96 0 nd nd
22 DB(a,e)P 0 0.30 1.52 0 nd nd
23 DB(a,i)P 0 0.84 2.76 0 nd nd
24 DB(a,h)P 0 0.57 1.88 0 nd nd
∑24 PAHs 26 (36.1%) - - 70.67 2.29 201.10

nd: not detected.

Table 6.

PAHs values determined in semi industrial Taftoon bread samples (n = 33).

NO. Compound Numbers of positive samples LOD
(ng/g)
LOQ
(ng/g)
Mean
(ng/g)
Min Level
(ng/g)
Max Level
(ng/g)
1 NPH 7 (21.2%) 1.49 4.91 46.39 5.09 241.15
2 ACL 0 0.65 2.50 0 nd nd
3 ACP 0 0.65 2.15 0 nd nd
4 FLR 0 0.75 2.48 0 nd nd
5 PHE 1 (3.0%) 0.61 2.01 6.76 - 6.76
6 ANT 3(9.1%) 0.56 1.85 10.89 10.73 11.12
7 FLA 0 0.14 0.46 0 nd nd
8 PYR 0 0.87 2.88 0 nd nd
9 B(c)F 0 0.18 0.60 0 nd nd
10 CP(c,d)P 0 0.82 2.71 0 nd nd
11 B(a)A 0 0.24 0.80 0 nd nd
12 CHR 0 0.20 0.67 0 nd nd
13 5-M-CHR 0 0.24 0.80 0 nd nd
14 B(b)F 0 0.35 1.15 0 nd nd
15 B(k)F 0 0.39 1.28 0 nd nd
16 B(a)P 0 0.79 2.59 0 nd nd
17 PER 0 0.39 1.29 0 nd nd
18 I(1,2,3-cd)P 0 0.56 1.85 0 nd nd
19 DB(a,h)A 0 0.36 1.19 0 nd nd
20 B(g,h,i)PER 0 0.58 1.90 0 nd nd
21 DB(a,l)P 0 0.59 1.96 0 nd nd
22 DB(a,e)P 0 0.30 1.52 0 nd nd
23 DB(a,i)P 0 0.84 2.76 0 nd nd
24 DB(a,h)P 0 0.57 1.88 0 nd nd
∑24 PAHs 11 (33.3%) - - 33.11 5.09 241.15

nd: not detected.

Bread’s contamination by PAHs could be due to both the contamination of bakery raw materials, such as water and primarily flour, and the baking process (23). Previous studies have shown that there are few published papers in field of PAHs in Iranian breads. Al-Rashdan et al. studied occurrence of 16 PAHs in different bread samples (15). Seven out of 18 samples were Iranian Bread baked from white flour using gas oven. They found NPH, FLR, and PHE were the most three abundant chemicals found in the studied breads. In addition, they reported that some Iranian bread samples had high levels of NPH and PHE. In Iran, most of traditional breads, including Taftoon and some semi-industrials are baked directly using high flame of gas in a short time. Therefore, we proposed that high levels of NPH and PHE could be because of direct flame gas in oven. These findings are in accordance with Rashdan et al. studies.

Eslamizad et al. developed a method for investigating BaP in famous Iranian traditional bread called Sangak (31). The collected and analyzed 29 Sangak bread samples from Tehran’s bread bakeries in 2014. Results showed that two Sangak samples were contaminated with BaP. Their another study showed that 35.5% and 13% of Sangak bread samples collected in Tehran and Shiraz were contaminated with BaP, respectively (23). In current study, BaP was not detected in Taftoon samples. Moreover, it has shown that the presence of PAHs in food is significantly due to heat processes such as smoking, smoke-drying, and grilling. However, environmental pollutants are also considered to be an issue (32). Based on the results of Rey-Salgueiro (13), direct toasting (flame-toasting, coal-grilling or gas oven-toasting) or indirect toasting (electric oven-toasting) would strongly affect in PAH levels in the final product.

Our results showed that beside the other routes, the detected PAHs in bread samples could be originated from gas oven. The efficiency of this route is dependent on various factors such as the type of energy used in heating (such as electricity, wood, flame, or solar energy), distance of heating, and design of the food device, which can further help foster the production of PAHs in food products (33).

Conclusion

In this study, a validated method based on QuEChERS sample preparation was applied for analysis of 24 PAHs in various traditional and semi-industrial Taftoon bread samples in Iran. For overcoming matrix effect, spiked calibration curves were used. According to the EU criteria, correlation coefficient, recovery percentage, and precision were acceptable for determination of PAHs in Taftoon bread. Analysis of Taftoon samples showed that three compounds; NPH, PHE, and ANT were found in 37 (35.2%) Taftoon samples. All of the obtained results were higher than the legal permissible limits (1.0 ng/g) proposed by the European Union for processed cereal-based foods. Our results showed that the detected PAHs in bread samples could be originated from gas oven.

Acknowledgments

Special thanks go to Arezoo Ebrahimi and Mahdi Samei for technical supports.

References

  • 1.Singh L, Varshney Jay G, Agarwal T. Polycyclic aromatic hydrocarbons’ formation and occurrence in processed food. Food Chem. . 2016;199:768–81. doi: 10.1016/j.foodchem.2015.12.074. [DOI] [PubMed] [Google Scholar]
  • 2.Ledesma E, Rendueles M, Díaz M. Benzo (a) pyrene penetration on a smoked meat product during smoking time. Food Addit. Contam. A . 2014:1688–98. doi: 10.1080/19440049.2014.949875. [DOI] [PubMed] [Google Scholar]
  • 3.International Agency for Research on Cancer. Agents classified by the IARC monographs. (2011) 1–109. World Health Organization. Lyon, France [Online]: Available from URL: https://monographs.iarc.fr/ [Google Scholar]
  • 4.Alexander J, Benford D, Cockburn A, Cravedi JP, Dogliotti E, Domenico AD, Fernández-Cruz ML, Fink-Gremmels J, Fürst P, Galli C, Grandjean P, Gzyl J, Heinemeyer G, Johansson N, Mutti A, Schlatter J, Leeuwen RV, Peteghem CV, Verger P. Polycyclic aromatic hydrocarbons in food scientific opinion of the panel on contaminants in the food chain. EFSA J. . 2008;724:1–114. [Google Scholar]
  • 5.Xia Z, Duan X, Qiu W, Liu D, Wang B, Tao S, Jiang Q, Lu B, Song Y and Hu X. Health risk assessment on dietary exposure to polycyclic aromatic hydrocarbons (PAHs) in Taiyuan, China. Sci. TotalEnviron. . 2010;408:5331–7. doi: 10.1016/j.scitotenv.2010.08.008. [DOI] [PubMed] [Google Scholar]
  • 6.Farhadian A, Jinap S, Faridah A, Zaidul ISM. Effects of marinating on the formation of polycyclic aromatic hydrocarbons (benzo[a]pyrene, benzo[b] fluoranthene and fluoranthene) in grilled beef meat. Food Control. . 2012;28:420–5. [Google Scholar]
  • 7.Purcaro G, Moret S, Conte LS. Overview on polycyclic aromatic hydrocarbons: occurrence, legislation and innovative determination in foods. Talanta . 2013;105:292–305. doi: 10.1016/j.talanta.2012.10.041. [DOI] [PubMed] [Google Scholar]
  • 8.Skaljac S, Petrovic L, Tasic T, Ikonic P, Jokanovic M, Tomovic V, Dzinic N, Sojic B, Tjapkin A, Skrbic B. Influence of smoking in traditional and industrial conditions on polycyclic aromatic hydrocarbons content in dry fermented sausages from Serbia. Food Control. . 2014;40:12–8. [Google Scholar]
  • 9.Li G, Wu Sh, Wang L, Akoh C. Concentration, dietary exposure and health risk estimation of polycyclic aromatic hydrocarbons (PAHs) in youtiao, a Chinese traditional fried food. Food Control. . 2016;59:328–36. [Google Scholar]
  • 10.Ciecierska M, Obiedzinski MW. Polycyclic aromatic hydrocarbons in the bakery chain. Food Chem. . 2013;141:1–9. doi: 10.1016/j.foodchem.2013.03.006. [DOI] [PubMed] [Google Scholar]
  • 11.Marti-Cid R, Llobet JM, Castell V, Domingo JL. Evolution of the dietary exposure to polycyclic aromatic hydrocarbons in Catalonia, Spain. Food Chem. Toxicol. . 2008;46:3163–71. doi: 10.1016/j.fct.2008.07.002. [DOI] [PubMed] [Google Scholar]
  • 12.Orecchio S, Papuzza V. Levels, fingerprint and daily intake of polycyclic aromatic hydrocarbons (PAHs) in bread baked using wood as fuel. J. Hazard. Mater. . 2009;164:876–83. doi: 10.1016/j.jhazmat.2008.08.083. [DOI] [PubMed] [Google Scholar]
  • 13.Rey-Salgueiro L, Garcia-Falcon MS, Martinez-Carballo E, Simal-Gandara J. Effects of toasting procedures on the levels of polycyclic aromatic hydrocarbons in toasted bread. J. Food Chem. . 2008;108:607–15. doi: 10.1016/j.foodchem.2007.11.026. [DOI] [PubMed] [Google Scholar]
  • 14.Plaza-Bolanos P, Garrido Frenich A, Martínez Vidal LM. Polycyclic aromatic hydrocarbons in food and beverages. Analytical methods and trends. J. Chromatogr. A . 2010;1217:6303–26. doi: 10.1016/j.chroma.2010.07.079. [DOI] [PubMed] [Google Scholar]
  • 15.Al-Rashdan A, Helaleh MI, Nisar A, Ibtisam A, Al-Ballam Z. Determination of the levels of polycyclic aromatic hydrocarbons in toasted bread using Gas Chromatography Mass Spectrometry. Int. J. Anal. Chem. . 2010;2010:1–8. doi: 10.1155/2010/821216. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 16.Ahmed MT, Abdel Hadi ES, Samahy SEl, Youssof K. The influence of baking fuel on residues of polycyclic aromatic hydrocarbons and heavy metals in bread. J. Hazard. Mater. . 2000;80:1–8. doi: 10.1016/s0304-3894(00)00300-9. [DOI] [PubMed] [Google Scholar]
  • 17.Shahabipour S, Khalighian N, Kobarfard F. Validation of an analytical method for determination of Benzo[a]pyrene bread using QuEChERS method by GC-MS. Iran.J. Pharm. Res. . 2016;15:465–74. [PMC free article] [PubMed] [Google Scholar]
  • 18.Poster DL, Schantz MM, Sander LC, Wise SA. Analysis of polycyclic aromatic hydrocarbons (PAHs) in environmental samples: a critical review of gas chromatographic (GC) methods. Anal. Bioanal. Chem. . 2006;386:859–81. doi: 10.1007/s00216-006-0771-0. [DOI] [PubMed] [Google Scholar]
  • 19.Veyrand B, Brosseaud A, Sarcher L, Varlet V, Monteau F, Marchand P, Andre F, Le Bizec B. Innovative method for determination of 19 polycyclic aromatic hydrocarbons in food and oil samples using gas chromatography coupled to tandem mass spectrometry based on an isotope dilution approach. J. Chromatogr. A . 2007;1149:333–44. doi: 10.1016/j.chroma.2007.03.043. [DOI] [PubMed] [Google Scholar]
  • 20.Ziegenhals K, Speer K, Jira W. Polycyclic aromatic hydrocaarbons (PAH) in chocolate on the German market. J. Consum. Prot.Food. S. . 2009;4:128–35. [Google Scholar]
  • 21.Coelho MS, Salas-Mellado MdlM. Effects of substituting chia (Salvia hispanica L ) flour or seeds for wheat flour on the quality of the bread. Food SciTechnol-LEB . 2015;60:729–36. [Google Scholar]
  • 22.Mohammadpour Karizaki V. Ethnic and traditional Iranian breads: different types, and historical and cultural aspects. J. Ethn. Foods . 2017;4:8–14. [Google Scholar]
  • 23.Eslamizad S, Kobarfard F, Javidnia K, Sadeghi R, Bayat M, Shahabipour S, Khalighian N, Yazdanpanah H. Determination of Benzo[a]pyrene in traditional, industrial and semi-industrial breads using a modified QuEChERS extraction, dispersive SPE and GC-MS and estimation of its dietary intake. Iran.J. Pharm. Res. . 2016;15:165–74. [PMC free article] [PubMed] [Google Scholar]
  • 24.Anastassiades M, Lehotay SJ, Stajnbaher D, Schenck FJ. Fast and easy multiresidue method employing acetonitrile extraction/partitioning and dispersive solid-phase extraction for the determination of pesticide residues in produce. J. AOAC Int. . 2003;86:412–31. [PubMed] [Google Scholar]
  • 25.European Commission. Document No. Sante/12682/2019: Method validation and quality control procedures for pesticide residues analysis in food and feed. Available from URL: http://www.eurl-pesticides.eu/docs/public/tmplt_article.asp?CntID=727.
  • 26.European Commission. 2002/657/EC: Commission Decision of 12 August 2002 implementing Council Directive 96/23/EC concerning the performance of analytical methods and the interpretation of results (Text with EEA relevance) (notified under document number C (2002) 3044). OJ L 220: 8-36. Available from URL: http://eur-lex.europa.eu/legal-content/EN/ALL/?uri=CELEX%3A32002D0657.
  • 27.Commission Regulation (EC) No 333/2007. Laying down the methods of sampling and analysis for the official control of the levels of lead, cadmium, mercury, inorganic tin, 3-MCPD and benzo(a)pyrene in foodstuffs. OJ L. 88:29–38. [Google Scholar]
  • 28.Chiu ML, Lawi W, Snyder ST, Wong PK, Liao JC, Gau V. Matrix effects- A challenge toward automation of molecular analysis. Technol. Rev. . 2017:233–42. [Google Scholar]
  • 29.Hajslova J, Zrostlikova J. Matrix effects in (ultra) trace analysis of pesticide residues in food and biotic matrices. J. Chromatogr. A . 2003;1000:181–97. doi: 10.1016/s0021-9673(03)00539-9. [DOI] [PubMed] [Google Scholar]
  • 30.Official Journal of the European Union. Commission Regulation (EC) No 1881/2006. Setting maximum levels for certain contaminants in foodstuffs. OJ L. 364:5–24. [Google Scholar]
  • 31.Eslamizad S, Yazdanpanah H, Javidnia K, Sadeghi R, Bayat M, Shahabipour S, Khalighian N, Kobarfard F. Validation of an analytical method for determination of Benzo[a]pyrene bread using QuEChERS method by GC-MS. Iran.J. Pharm. Res. . 2016;15:465–74. [PMC free article] [PubMed] [Google Scholar]
  • 32.Bansal V, Kim KH. Review of PAH contamination in food products and their health hazards. Environ. Int. . 2015;84:26–38. doi: 10.1016/j.envint.2015.06.016. [DOI] [PubMed] [Google Scholar]
  • 33.Simko P. Determination of polycyclic aromatic hydrocarbons in smoked meat products and smoke flavouring food additives. J. Chromatogr. B . 2002;77:3–18. doi: 10.1016/s0378-4347(01)00438-8. [DOI] [PubMed] [Google Scholar]

Articles from Iranian Journal of Pharmaceutical Research : IJPR are provided here courtesy of Brieflands

RESOURCES