Investigating the effect of Flavor variation on the concentration of Lead and Cadmium in Potato chips products
Alaa Alassaf, Lina Soubh
University in Damascus, Syria – Damascus.
*Corresponding Author E-mail: alaa.alassaf.97@gmail.com, lina.soubh@damascusuniversity.edu.sy
ABSTRACT:
Potato chips products are considered highly consumed food around the world especially for children. Therefore, there are concerns about these products because it may contaminated with heavy metals that can accumulate in human body, causing a threat to human health and may cause some diseases. This study was conducted to measure Lead (Pb) and Cadmium (Cd) concentrations in these products in four flavors (salted, cheese, hot and barbeque) in three brands (A, B and C) manufactured and consumed in Syria. Samples were digested with wet oxidation method using concentrated nitric acid and hydrogen peroxide, then the concentrations of the mentioned metals were measured with Graphite Furnace Atomic Absorption Spectrophotometer (GF-AAS). The results of this study showed that the average concentration of Pb in potato chips are ranged between 0.01448 to 0.18013 mg/kg, and the average concentration of Cd are ranged between 0.03136 to 0.2733mg/kg. The levels of lead and cadmium in potato chips exceeded the acceptable limit according to Codex Alimentarius standards in some samples. Statistical analysis Kruskal-Wallis H test between the four flavors of potato chips shows that the difference in the concentration of Pb and Cd may be due to the difference in flavor in samples (p-value < 0.05).
KEYWORDS: Potato chips, Flavor, Lead, Cadmium, Heavy metals.
INTRODUCTION:
Potato chips are a popular snack for many people around the world and a dietary source of carbohydrates, protein, and essential nutrients1. Their consumption has been increasing over the years especially for children causing them obesity2,3. There are many flavors of potato chips available to meet different preferences1.
Manufacturing potato chips involves a series of steps, starting with selecting potatoes (solanum tuberosum)4, cutting them into thin slices, deep-frying them, adding different seasonings, and packaging the final product5.
However, concerns have been raised about the presence of heavy metals in food6. It may contaminate potato chips through soil or environmental pollution and pesticides, the production process, and contamination of seasoning and packaging7.
Heavy metals -such as lead, cadmium, mercury and arsenic8- can have negative health effects when consumed in large quantities, due to their ability to accumulate in tissues over time and cause a range of health problems9,10, include organ damage, growth problems in children, and cancer10. Other heavy metals that considered to be essential to the body and have important role in biological systems, but they became toxic if exceed the permitted levels, such as copper, zinc, iron and manganese1.
Lead contamination in food can occur through lead-based paints, contaminated soil, water pipes, and food packaging materials11,12. High levels of Lead exposure can cause neurological damage12,13, and chronic exposure to low levels may affect children's development, the reproductive system, and various other health problems9,12. Cadmium found in industrial processes, such as battery manufacturing and metal plating. It can also be found in fertilizers and pesticides used in agriculture7,12. It can accumulate in crops like rice, leafy vegetables, and root crops, as well as in shellfish and crustaceans. Long-term exposure to cadmium can lead to kidney damage, bone disorders, and an increased risk of certain cancers6,7,12,13.
Therefore, there is always a need to detect these elements to reduce exposure, especially in children. This study aimed to determine the concentrations of Cadmium and Lead using graphite furnace atomic absorption spectroscopy (GF-AAS) in potato chips manufactured in Syria to determine whether they exceed the acceptable limits, in addition to studying the effect of different flavors on the concentrations of these two elements.
MATERIALS AND METHODS:
Reagents:
All the reagents were of analytical grade. Double deionized water was used for dilution and preparation of reagents and standards. All the plastic and glassware were cleaned by soaking in dilute nitric acid 2% for 24 hours and were rinsed with distilled water prior to use and dried to ensure that any contamination does not occur.
Sample collection:
Commercially three popular brands of potato chips (coded as A, B and C) were randomly purchased from several markets in Damascus, Syria, and they were divided into 4 groups according to flavor (salt, cheese, barbeque and hot).
Sample digestion:
Wet digestion of the samples was performed14,15 using a mixture of nitric acid and hydrogen peroxide (3:1) (16 ml for 5.0g sample). This mixture was heated up to 130°C for 1 h, after cooling 10ml of double deionized water was added to the sample and mixed. The residue was filtered through Whatman filter paper No. 41. The sample was then diluted to 100mL with double deionized water.
Blank samples that contain 12.0mL of nitric acid and 4.0 mL of hydrogen peroxide were prepared in the same procedure as real samples.
Analysis of samples:
The samples were analyzed by GF-AAS to determine the heavy metals concentration16,17. Working conditions of GF-AAS are shown in (Table 1).
Table 1. Instrument operating conditions for the determination of heavy metals in samples by GF-AAS.
|
Element |
Wavelength (nm) |
Lamp current (mA) |
Slit width (nm) |
Detection limit (μg/L) |
|
Pb |
283.3 |
7.5 |
1.3 |
0.3 |
|
Cd |
228.8 |
7.5 |
1.3 |
0.01 |
All standards and samples were analyzed in triplicates. The value of heavy metals concentration in potato chips (mg/L) was applied into following equation Eq. (1) to obtain the actual concentration of heavy metals present in the samples (mg/kg).
Heavy metal concentration in potato chips1,
C x A
Mg/kg = ----------- (1)
W
Where, C = Heavy metal concentration in potato chips (mg/L); A = Final volume of diluted sample; W = weight of sample (g).
RESULT:
Lead concentrations in potato chips samples:
(Table 2) and (Figure 1) show the concentrations of lead in commercial brands of potato chips and the difference in concentration of lead according to flavor. Results are expressed as the average of the triplicate analyses.
The concentrations of lead in potato chips were ranged between 0.01448 to 0.18013mg/kg. Barbeque flavor of brand B showed the highest concentration, and exceeded the maximum permitted level for lead by Codex Alimentarius18.
Table 2. Mean lead concentrations (mg/kg) of potato chips samples (Data are presented as means±SD, n = 5)
|
Brand |
Flavor |
Pb |
|
A |
Salted |
0.01856 ± 0.0014 |
|
Cheese |
0.01568 ± 0.009 |
|
|
Hot |
0.0196 ± 0.0024 |
|
|
Barbeque |
0.01748 ± 0.0016 |
|
|
B |
Salted |
0.03508 ± 0.0046 |
|
Cheese |
0.03232 ± 0.0054 |
|
|
Hot |
0.01752 ± 0.0017 |
|
|
Barbeque |
0.17032 ± 0.0079* |
|
|
C |
Salted |
0.01928 ± 0.0013 |
|
Cheese |
0.02804 ± 0.0041 |
|
|
Hot |
0.02524 ± 0.0025 |
|
|
Barbeque |
0.02804 ± 0.0029 |
|
|
Permitted level by Codex Alimentarius |
0.1a |
|
* Exceed the maximum permitted level of Codex Alimentarius.
a Maximum permitted level root and tuber vegetables.
Figure 1. Concentration of lead (Pb) in potato chips samples
Cadmium concentrations in potato chips samples:
(Table 3) and (Figure 2) show the concentrations of cadmium in commercial brands of potato chips and the difference in concentration of Cadmium according to flavor. Results are expressed as the average of the triplicate analyses.
Table 3. Mean cadmium concentrations (mg/kg) of potato chips samples (Data are presented as means ± SD, n = 5)
|
Brand |
Flavor |
Cd |
|
A |
Salted |
0.113 ± 0.0034* |
|
Cheese |
0.07416 ± 0.0098 |
|
|
Hot |
0.06228 ± 0.0065 |
|
|
Barbeque |
0.05004 ± 0.0135 |
|
|
B |
Salted |
0.06716 ± 0.0108 |
|
Cheese |
0.08824 ± 0.0053 |
|
|
Hot |
0.08484 ± 0.004 |
|
|
Barbeque |
0.12336 ± 0.0025* |
|
|
C |
Salted |
0.25456 ± 0.0068* |
|
Cheese |
0.15188 ± 0.0023* |
|
|
Hot |
0.27028 ± 0.0029* |
|
|
Barbeque |
0.21184 ± 0.0025* |
|
|
Permitted level by Codex Alimentarius |
0.1a |
|
* Exceed the maximum permitted level of Codex Alimentarius.
a Maximum permitted level root and tuber vegetables.
The concentrations of cadmium in potato chips were ranged between 0.03136 to 0.2733 mg/kg. Salted flavor of brand A, barbeque flavor of brand B and all samples of brand C exceeded the maximum permitted level for Cd by Codex Alimentarius18.
Figure 2. Concentration of Cadmium (Cd) in potato chips samples
The previous results show the difference between the concentrations of the studied elements according to the brand of potato chips and the difference in flavor for each group. This is consistent with previous studies conducted on potato chips and the effect of the difference in flavor on these elements.
Contamination of potato chip products with lead and cadmium may be attributed to contamination of raw materials involved in manufacturing, such as soil, the type of potatoes used, added seasoning, the manufacturing process, and contact with surfaces.
By applying the statistical analysis Kruskal-Wallis H test between the four flavors of potato chips, it is noted from the (Table 4) that there is statistical difference (H value > chi square) between flavors in the same brand, which indicates that the difference of lead and cadmium concentration caused by added seasoning. All p-values are less than 0.05 which mean the results are statistically significant.
Table 4. Statistical analysis between the four flavors of potato chips samples, (N=40, df=3, α=0.05)
|
Elment |
Brand |
Flavor |
Mean ± SD |
Min conc. |
Max conc. |
H value |
chi square |
p value |
|
mg/kg |
mg/kg |
mg/kg |
||||||
|
Pb |
A |
Salted |
0.0185 ± 0.0014 |
0.0165 |
0.0203 |
9.495 |
7.815 |
0.023 |
|
Cheese |
0.0156 ± 0.009 |
0.0144 |
0.0168 |
|||||
|
Hot |
0.0196 ± 0.0024 |
0.0163 |
0.0224 |
|||||
|
Barbeque |
0.0174 ± 0.0016 |
0.0156 |
0.0197 |
|||||
|
B |
Salted |
0.035 ± 0.0046 |
0.0294 |
0.0404 |
15.945 |
7.815 |
0.001 |
|
|
Cheese |
0.0323 ± 0.0054 |
0.0254 |
0.0405 |
|||||
|
Hot |
0.0175 ± 0.0017 |
0.0155 |
0.0194 |
|||||
|
Barbeque |
0.1703 ± 0.0079 |
0.1612 |
0.1801 |
|||||
|
C |
Salted |
0.0192 ± 0.0013 |
0.0177 |
0.0213 |
11.977 |
7.815 |
0.007 |
|
|
Cheese |
0.028 ± 0.0041 |
0.0221 |
0.0325 |
|||||
|
Hot |
0.0252 ± 0.0025 |
0.0217 |
0.0286 |
|||||
|
Barbeque |
0.028 ± 0.0029 |
0.0246 |
0.0322 |
|||||
|
Cd |
A |
Salted |
0.113 ± 0.0034 |
0.1076 |
0.1162 |
14.431 |
7.815 |
0.002 |
|
Cheese |
0.0741 ± 0.0098 |
0.0595 |
0.0843 |
|||||
|
Hot |
0.0622 ± 0.0065 |
0.0521 |
0.0702 |
|||||
|
Barbeque |
0.05 ± 0.0135 |
0.0313 |
0.0641 |
|||||
|
B |
Salted |
0.0671 ± 0.0108 |
0.0569 |
0.0832 |
15.192 |
7.815 |
0.001 |
|
|
Cheese |
0.0882 ± 0.0053 |
0.0828 |
0.0943 |
|||||
|
Hot |
0.0848 ± 0.004 |
0.0785 |
0.0886 |
|||||
|
Barbeque |
0.1233 ± 0.0025 |
0.1171 |
0.1295 |
|||||
|
C |
Salted |
0.2545 ± 0.0068 |
0.2446 |
0.2623 |
17.655 |
7.815 |
0.0005 |
|
|
Cheese |
0.1518 ± 0.0023 |
0.1482 |
0.1546 |
|||||
|
Hot |
0.2702 ± 0.0029 |
0.2665 |
0.2733 |
|||||
|
Barbeque |
0.2118 ± 0.0025 |
0.2087 |
0.2152 |
CONCLUSION:
The results of the study showed that the Lead concentrations in potato chips samples did not exceed the permitted limit by Codex Alimentarius (0.1ppm), except for the barbeque flavor of brand B, which exceeded the permissible limit by average of 0.07 ppm of lead concentration.
Cadmium concentrations in all samples of brand C, Salted flavor of brand A and barbeque flavor of brand B has exceeded the permitted limit by Codex Alimentarius (0.1ppm). This may cause many health problems when consuming these products in large quantities especially for children, because these elements have the ability to accumulate in the body’s tissues and cause mental and growth problems19.
In addition, the statistical study showed that there were statistically significant differences between the studied flavor groups (p value < 0.05), which may indicate that the difference in the concentrations of the studied elements may be due to the added seasonings used by each brand.
CONFLICT OF INTEREST:
The authors have no conflicts of interest regarding this investigation.
REFERENCES:
1. Ahmed YH, et al. Heavy metals content in some chips products in Iraqi markets. Iraqi Journal of Science. 2016; 57(4C): 2818-2828.
2. Soumia MD, Darwish MA. Survey Detection of Trace Heavy Metals in Potato chips and Ice Cream from Assiut Governorate, Egypt. Journal of Food and Dairy Sciences. 2012; Oct; 3(10): 541-551. doi: 10.21608/JFDS.2012.81665
3. Kamrun N, et al. Childhood Obesity Status in Australia: A Recent Perspective. Research Journal of Pharmacy and Technology. 2017; Aug 1; 10(8): 2727-2734. doi: 10.5958/0974-360X.2017.00500.5
4. Koushika D, et al. A review on pharmacological properties of Solanum tuberosum. Research Journal of Pharmacy and Technology. 2017; May 1; 10(5): 1517-1522. doi: 10.5958/0974-360X.2017.00267.0
5. Bakr AA, Gawish RA. Technological evaluation of new cultivars for potato chips manufacturing. Food/Nahrung. 1992; 36(4): 380-387. doi: https://doi.org/10.1002/food.19920360409
6. Safa WA. Study of Heavy Metals and their effects on Oxidant / Antioxidant Status in Workers of fuel Station in Hilla city-Iraq. Research Journal of Pharmacy and Technology. 2018; Jan 1; 11(1): 312-316. doi: 10.5958/0974-360X.2018.00057.4
7. Pawaskar SM. Khan S. Heavy Metal Analysis of the leaf extracts of some Indian Medicinal Plants from Western Maharashtra. Research Journal of Pharmacy and Technology. 2023; 16(6): 2801-2807. doi: 10.52711/0974-360X.2023.00461
8. Rajeshwari BM. PatilS J. Heavy Metals Status in Soils of Ballari District using Atomic Absorption Spectroscopy (AAS). Asian Journal of Research in Chemistry. 2018; Aug; 11(4): 701-704. doi: 10.5958/0974-4150.2018.00123.2
9. Santhosh KR, Asha DS. Lead Toxicity on Male Reproductive System and its Mechanism: A Review. Research Journal of Pharmacy and Technology. 2018; Mar 1; 11(3): 1228-1232. doi: 10.5958/0974-360X.2018.00228.7
10. Patil PM, et al. Bioaccumulation of Cadmium Chloride in the Fresh Water Fish Cattle-Cattle. Research Journal of Pharmacy and Technology. 2011; Jan 1; 4(1): 121-123.
11. Ragadevan V, et al. Removal of Heavy Metal Ions (Lead) using Natural Adsorbent. Research Journal of Pharmacy and Technology. 2019; Aug 1; 12(8): 3693-3696. doi: 10.5958/0974-360X.2019.00631.0
12. Laxmi S, Namrata J. A Review on Soil Heavy metals Contamination: Effects, Sources and Remedies. Asian Journal of Research in Chemistry. 2020; Aug; 13(4): 299-304. doi: 10.5958/0974-4150.2020.00058.9
13. Klaassen CD. Toxic Effects of Metals. In: Casarett and Doull's toxicology: the basic science of poisons. McGraw-Hill, New York. 2013; 8th ed: 981-996
14. Sapna S, et al. Elemental Analysis in Piper betle Linn. and Jatropha gossypifolia Linn. leaves: Biosafety Studies. Research Journal of Pharmacy and Technology. 2018; Nov 1; 11(11): 5078-5082. doi: 10.5958/0974-360X.2018.00926.5
15. Antakli S, et al. Sample Microwave Digestion for the Determination of Manganese, Iron, Zinc, Copper and Nickel in Catfish Consumed in Syria by Flame Atomic Absorption Spectrometry. Research Journal of Pharmacy and Technology. 2018; May 1; 11(5): 2094-2099. doi: 10.5958/0974-360X.2018.00388.8
16. Venugopal NVS., et al. Trace Element Levels in Fruits and Vegetable by using Atomic Absorption Spectrophotometer (AAS). Asian Journal of Research in Chemistry. 2011; Nov; 4(11): 1769-1771.
17. Bais SK., et al. Comparative Evaluation of Heavy Metals in Marketed Haematinic Herbal Formulations by Atomic Absorption Spectroscopy. Asian Journal of Pharmaceutical Analysis. 2014; Mar 10; 4(1): 11-16.
18. Food and Agricultural Organization / World Health Organization (FAO/WHO) (2019). List of Maximum Levels for Contaminants and Toxins in Foods, Yogyakarta: World Health Organization.
19. Kadhem WM., Enaya H. Effect of Lead and Aluminium in the levels of Dopamine and Acetylcholine in the Brain Male Rats. Research Journal of Pharmacy and Technology. 2018; May; 11(5): 2055-2057. doi: 10.5958/0974-360X.2018.00381.5
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Received on 06.07.2024 Revised on 03.10.2024 Accepted on 09.12.2024 Published on 20.01.2025 Available online from January 27, 2025 Research J. Pharmacy and Technology. 2025;18(1):139-142. DOI: 10.52711/0974-360X.2025.00021 © RJPT All right reserved
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