Acessibilidade / Reportar erro

Development of an Analytical Method for the Determination of Metals in Chicken Breast by Microwave Induced Plasma Optical Emission Spectrometry (MIP-OES)

Abstract

An analytical method for the determination of Al, Ca, Cd, Cr, Cu, Fe, Hg, K, Mg, Na and Zn in breast of conventional, country and Christmas chicken and turkey samples using microwave induced plasma optical emission spectrometry (MIP-OES) technique was developed. Samples were decomposed in a digester block with a reflux system under conditions optimized using a central composite design as it follows: 2 g of sample, in 7.5 mL of HNO3 during 180 min at 160 °C. The accuracy was evaluated by the analysis of standard reference material SRM 1546 meat homogenate (94 to 108%) and also by addition and recovery tests (80 to 121%). The highest concentrations, in mg kg-1, of Al (2.77), Ca (88.3), Cu (1.99), Fe (3.65), K (3236), Mg (292.62) and Na (312.03) were found in the breast of conventional chicken sample. Zinc presented high value in the breast of turkey sample (10.6 mg kg-1). However, the found concentrations were lower than the daily consumption limit established by supervisory agencies and reference limits from Brazilian legislation. Cadmium, Cr and Hg presented values below limit of quantification. In this way, it is evident that chicken breast should be consumed in a complementary way in a healthy diet.

Keywords:
chicken breast; acid decomposition; metals; MIP-OES


Introduction

According to the Brazilian Animal Protein Association (ABPA), few countries in the world have the propensity that Brazil naturally achieved to be recognized internationally as the “Barn of the World” due to extensive grain fields with fertile land and an exceptionally favorable climate. Brazil has also compromised itself as a partner in food security in several countries around the world.11 Brazilian Association of Animal Protein (ABPA); Brazilian Chicken; available at http://www.brazilianchicken.com.br/en and http://abpa-br.com.br/storage/files/relatorio-anual-2018.pdf accessed in June 2019.
http://www.brazilianchicken.com.br/en an...

Since the 1980s, the meat segment in Brazil has been very dynamic in relation to production, consumption and foreign trade. Particularly noteworthy is the poultry sector, which has expanded both in terms of slaughter and exports, as it is very competitive and integrated with the foreign market.22 Empresa Brasileira de Pesquisa Agropecuária (EMBRAPA); Embrapa Suínos e Aves; available at https://www.embrapa.br/suinos-e-aves accessed in June 2019.
https://www.embrapa.br/suinos-e-aves...
Approximately 70% of the Brazilian chicken exports are concentrated in the Southern part of the country (Santa Catarina and Rio Grande do Sul states).11 Brazilian Association of Animal Protein (ABPA); Brazilian Chicken; available at http://www.brazilianchicken.com.br/en and http://abpa-br.com.br/storage/files/relatorio-anual-2018.pdf accessed in June 2019.
http://www.brazilianchicken.com.br/en an...
,22 Empresa Brasileira de Pesquisa Agropecuária (EMBRAPA); Embrapa Suínos e Aves; available at https://www.embrapa.br/suinos-e-aves accessed in June 2019.
https://www.embrapa.br/suinos-e-aves...

Chicken meat, besides being tasty, has other attractive features, such as affordable prices and high nutritional content.33 Pereira, T. E. J.; Ströher, G. R.; Turbiani, F. R. B.; Braz. J. Food Technol.. 2013, 16, 278.,44 Bohrer, B. M.; Trends Food Sci. Technol.. 2017, 65, 103. According to the United States Department of Agriculture (USDA),55 United States Department of Agriculture (USDA); https://ndb.nal.usda.gov/ndb/ accessed in June 2019.
https://ndb.nal.usda.gov/ndb/...
chicken meat and offals are rich in protein as well as in vitamins, and present minerals such as Ca, Fe, Mg, P, K, Zn, Mn and Se. The low-fat content of chicken breast meat is also another important reason for those seeking a healthier diet.66 Milicevic, D.; Trbovic, D.; Petrovic, Z.; Jakovac-Strajn, B.; Nastasijevic, I.; Koricanac, V.; Proc. Food Sci.. 2015, 5, 191.

7 Chen, S.; Lin, Y.; Kao, Y.; Shih, Y.; Food Addit. Contam., Part B. 2013, 6, 231.
-88 da Silva, D. C. F.; de Arruda, A. M. V.; Gonçalves, A. A.; J. Food Sci. Technol.. 2017, 54, 1818.

According to the ABPA report,11 Brazilian Association of Animal Protein (ABPA); Brazilian Chicken; available at http://www.brazilianchicken.com.br/en and http://abpa-br.com.br/storage/files/relatorio-anual-2018.pdf accessed in June 2019.
http://www.brazilianchicken.com.br/en an...
the chicken meat per capita consumption in 2017 reached 42.07 kg a year. Due to the high consumption of chicken meat and also to the increase in exports, there is a requirement regarding the food security of chicken meat. Generally, chickens and turkey are reared in intensive farms and their feeding can contain additives. In this way, the mineral content of meat varies depending on the breed, rearing, diet, cut and carcass processing.99 Cabrera, M. C.; Ramos, A.; Saadoun, A.; Brito, G.; Meat Sci.. 2010, 84, 518.

Food composition data are important for estimating the adequacy of essential nutrient intake and for assessing the risks of exposure, mainly from the ingestion of potentially toxic elements. Food intake is a mean of exposure to metals because they are naturally constituents of foodstuffs, but it can also happen by environmental contamination or contamination during processing.99 Cabrera, M. C.; Ramos, A.; Saadoun, A.; Brito, G.; Meat Sci.. 2010, 84, 518. The elements can be classified as non-essential (Al, As, Cd, Pb, Hg, etc.) and essential (Fe, Mn, Cu, Zn, Se, among others). Potentially toxic elements can be harmful even at low concentrations when ingested over a long period of time. An interesting case is found for the As. Hunter1010 Hunter, P.; Eur. Mol. Biol. Organ. 2008, 9, 15. in a report mentions that As can be considered as a micronutrient in animals and Zheng et al.1111 Zeng, H.; Uthus, E. O.; Combs, G. F.; Inorg. Biochem.. 2005, 99, 1269. related an interaction of As with Se. The recommended daily intake of As should be smaller than Se (40 μg per day). The essential elements may also produce toxic effects when ingested in excess.1212 Uluozlu, O. D.; Tuzena, M.; Mendil, D.; Soylak, M.; J. Hazard. Mater.. 2009, 163, 982.,1313 Celik, U.; Oehlenschlager, J.; Food Control. 2007, 18, 258. The literature reports few studies of chicken meat that evaluates the metal concentrations. Hu et al.1414 Hu, Y.; Zhang, W.; Chen, G.; Cheng, H.; Tao, S.; Environ. Pollut.. 2018, 234, 667. determined trace metals (Cu, Zn and As) in fresh chicken meat products. Menezes et al.1515 Menezes, E. A.; Oliveira, A. F.; França, C. J.; Souza, G. B.; Nogueira, A. R. A.; Food Chem.. 2018, 240, 75. evaluated the bioaccessibility of Ca, Cu, Fe, Mg and Zn in beef, pork and chicken samples. Wu et al.1616 Wu, Y.; Zhanh, H.; Liu, G.; Zhang, J.; Wang, J.; Yu, Y.; Lu, S.; Chemosphere. 2016, 144, 564. evaluated the concentration of trace elements as Cd, Hg, Pb, As, Cr, Cu, Fe, Zn, etc. in chicken meat products by inductively coupled plasma mass spectrometry (ICP-MS).

The quantification of metals in food samples is usually carried out by atomic spectrometry techniques. The microwave induced plasma optical emission spectrometry (MIP-OES) provides multi-element analysis and sequential measurements. Can be highlighted due to low operational cost, since the plasma is maintained through nitrogen removed from the atmospheric air and does not require flammable or expensive gases such as acetylene, nitrous oxide or argon, besides exhibits limits of detection close to the techniques of flame atomic absorption spectrometry (FAAS) and inductively coupled plasma optical emission spectrometry (ICP-OES).1717 Ríos, S. E. G.; Peñuela, G. A.; Botero, C. M. R.; Food Anal. Methods. 2017, 10, 3407.

18 de Souza, A. O.; Pereira, C. C.; Heling, A. I.; Oreste, E. Q.; Cadore, S.; Vieira, M. A.; Ribeiro, A. S.; J. Food Compos. Anal.. 2019, 77, 60.

19 Matusiewicz, H.; Slachcinski, M.; J. Braz. Chem. Soc.. 2016, 27, 584.
-2020 Machado, R. C.; Amaral, C. D. B.; Nóbrega, J. A.; Nogueira, A. R. A.; J. Agric. Food Chem.. 2017, 65, 4839.

The sample preparation is the most important step of a chemical analysis and there is no universal procedure that can be used in samples of different compositions. Thus, it is typical of the field of analytical chemistry to perform sequential studies on new systems and/or sample preparation methods in order to expand their working capacity. Reflux systems for acid decomposition have recently been applied, providing satisfactory results for the determination of metal and volatile elements in different samples.2121 Oreste, E. Q.; de Jesus, A.; de Oliveira, R. M.; da Silva, M. M.; Vieira, M. A.; Ribeiro, A. S.; Microchem. J.. 2013, 109, 5.

22 de Oliveira, R. M.; Antunes, A. C. N.; Vieira, M. A.; Medina, A. L.; Ribeiro, A. S.; Microchem. J.. 2016, 124, 402.

23 Pereira, C. C.; de Souza, A. O.; Oreste, E. Q.; Cidade, M. J. A.; Cadore, S.; Ribeiro, A. S.; Vieira, M. A.; J. Braz. Chem. Soc.. 2016, 27, 685.
-2424 Oreste, E. Q.; de Souza, A. O.; Pereira, C. C.; Lisboa, M. T.; Cidade, M. J. A.; Vieira, M. A.; Cadore, S.; Ribeiro, A. S.; Food Anal. Methods. 2015, 9, 777. The cold finger (reflux system) provide a larger surface area for the condensation and allow the formation of the absorber solution film for better retention of the volatile species. In this way, losses of analyte by volatilization and reposition of acids are avoided, increasing the efficiency of decomposition.2121 Oreste, E. Q.; de Jesus, A.; de Oliveira, R. M.; da Silva, M. M.; Vieira, M. A.; Ribeiro, A. S.; Microchem. J.. 2013, 109, 5.

Considering the importance of chicken meat food security, the present study aims to develop an analytical method for the quantification of Al, Ca, Cd, Cr, Cu, Fe, Hg, K, Mg, Na and Zn in chicken breast samples (conventional chicken, country and Christmas chicken and turkey) by MIP-OES. The acid decomposition with the reflux system was employed and the best conditions were optimized using a central composite design (CCD).

Experimental

Instrumentation

The measurements were carried out using a 4200-MIP-OES (Agilent Technologies, Melbourne, Australia) equipped with a nitrogen generator model 4107 (Melbourne, Australia). The nebulizer flow rate was variable for each analyte (Table S1, Supplementary Information (SI) section). Two sample introduction systems were employed: a double-pass cyclonic chamber and the inert OneNeb nebulizer and also a multimode sample introduction system (MSIS) that allows simultaneous nebulization and vapor generation. All measurements were performed in triplicate. The integration time was 10 s and the stabilization time was 15 s. Instrumental parameters such as nebulizer gas pressure and viewing position were automatically optimized, for each analyte separately, using the instrument software (MP Expert). The background correction was performed automatically by the software.

For sample decomposition, a digester block was employed (MA-4025 model, Marconi, Piracicaba, SP, Brazil). In each digester tube, a cold finger with continuous water recirculation (ca. 15 ºC) was introduced to avoid losses by volatilization of analytes and reagents, as described in a previous work.2121 Oreste, E. Q.; de Jesus, A.; de Oliveira, R. M.; da Silva, M. M.; Vieira, M. A.; Ribeiro, A. S.; Microchem. J.. 2013, 109, 5. More details of the reflux system can be found in Figure S1 (SI section).

Reagents and samples

All reagents used were of analytical grade. Solutions used were prepared with deionized water obtained by a water distiller MA078 (Marconi, Piracicaba, SP, Brazil) and subsequently deionized by passing through a column CS1800 (Permution, Curitiba, PR, Brazil). Calibrations solutions were prepared from a multielement standard solution 6 for ICP (Sigma Aldrich, Buchs, Switzerland) containing 100 mg L-1 of each analyte. The nitric acid (Synth, Diadema, SP, Brazil) was purified by doubly subboiling distillation in a quartz system (Marconi, model MA-075, Piracicaba, SP, Brazil). For multimode sample introduction system was used NaBH4 0.5% (m/v) in NaOH 0.5% (m/v). For carbon analysis was used a stock solution of dextrose (Synth, Diadema, SP, Brazil). A standard reference material SRM 1546 Meat Homogenate produced by the National Institute of Standards and Technology (NIST, Gaithersburg, MD, USA) was used for accuracy evaluation. The SRM 1546 is a mixture of pork, mechanically-separated chicken, ham, salt, sucrose, water, and spices.

Samples of conventional chicken, country chicken, Christmas chicken and turkey were acquired in a local supermarket of Pelotas, RS, Brazil. At the laboratory, the samples were initially cut, the breast was separated and homogenized using a blender (non-contaminated kitchen mixer), put into clean plastic containers and frozen at -16 °C. Chicken breast samples were defrosted just before the sample preparation step. All results were expressed in wet mass.

Optimization procedures

The optimal conditions for acid decomposition procedure were performed by factorial design experiments considering the following variables: HNO3 volume, decomposition time and decomposition temperature (Table S2, SI section). For the method development, a conventional chicken breast sample was used, and the sample mass was fixed in 2 g. The variables ranges were based on preliminary experiments. A central composite design (CCD) was applied (23 factorial, with three central points and six axial points) providing a total of 17 randomly performed experiments. Also, the residual carbon was determined because is an important parameter to evaluate the sample decomposition efficiency, besides being an essential criterion to be controlled depending on the instrumental technique employed.2525 Gouveia, S. T.; Silva, F. V.; Costa, L. M.; Nogueira, A. R. A.; Nóbrega, J. A.; Anal. Chim. Acta. 2001, 445, 269. All results were analyzed using the software Statistica® 7.0,2626 Statistica 7.0 software; Statsoft Inc., Tulsa, OK, USA, 2004. considering a significance level of 90%. For these optimizations, the conventional nebulization for sample introduction into the plasma was employed.

Sample preparation procedure

Aliquots of 2 g of chicken breast samples were weighed directly into a glass digester tube, and 7.5 mL of 65% HNO3 (m/m) was added. The reflux system was then coupled to the digester tubes, and the mixture was heated in a digester block at 160 °C during 180 min. The decomposition was considered complete when the entire sample was dissolved. After cooling, the resulting solution was transferred to a polypropylene flask and filled up to a volume of 50 mL with deionized water. For analysis, the solutions were diluted two times. All samples were prepared in triplicate, and analytical blanks were prepared using the same procedure.

Figures of merit evaluated in this work were: limits of detection (LOD), limits of quantification (LOQ), linearity and accuracy. The procedures were performed in compliance with the INMETRO guide.2727 Instituto Nacional de Metrologia, Qualidade e Tecnologia (INMETRO); Orientação sobre Validação de Métodos de Ensaios Químicos, DOQ-CGCRE-008, rev. 2; INMETRO: Rio de Janeiro, 2007, p. 14. The linear range employed for Al, Ca, Cd, Cr, Cu, Fe, Hg, K, Mg, Na and Zn was: 0.5 to 5.0 mg L-1 (conventional nebulization) and 10 to 250 μg L-1 (multimode sample introduction system) and for C, 0.05 to 1.0%. For the elements that were not determined in the SRM 1546 (Al, Cd, Cr, Cu and Hg), the addition and recovery tests were applied at three concentration levels: 0.75; 2.5 and 4.0 mg L-1 for conventional nebulization and 20; 65 and 170 μg L-1 for the multimode sample introduction system. The difference between the concentration averages found for the metals in the breast samples were evaluated by the Tukey’s test, with a significance level of 5%. The statistical analysis was performed using the Origin software tool.2828 OriginPro v8.0724; OriginLab, Northampton, USA, 2007.

Results and Discussion

Optimization of decomposition procedure

The best conditions for acid decomposition with reflux system of chicken breasts were selected using factorial design experiments considering the following variables: HNO3 volume, temperature of digester block and decomposition time. The matrix of the full factorial design containing the data for Al, Ca, Cu, Fe, K, Mg, Na and Zn, as well as intensity as the analytical response, is shown in Table S3 (SI section). Also, are presented the results for C concentration that was used in order to evaluate the efficiency of the sample decomposition.

The results evaluated using a Pareto chart (Figure S2, SI section), demonstrated that for Al, Cu, Fe, K and Zn no variable was statistically significant considering a 90% confidence level. Considering the significant variables only, an analysis of variance (ANOVA) was applied for Ca, Mg, Na and C (Table S4, SI section). The results showed that the models are significant and adequate to describe the results through the surface response graphics, as is evident by the F value calculated.

The Figure 1 shows the generated surface response graphics at the levels studied for each analyte and the Figure 2 shows the surface response graphics obtained for C. For Ca (Figure S3, SI section), was observed that the interaction between the variables HNO3 volume and decomposition time were statistically significant; for Na, only the variable HNO3 volume and for Mg, the temperature of digester block. All variables were statistically significant for C. The analysis of surface response graphics indicated that highest intensity was obtained in the follow conditions: 7.5 mL of HNO3 for Na and Ca; decomposition time of 180 min for Ca and C and, temperature of digester block at 160 °C for Mg and C.

Figure 1
Surface response obtained from the central composite design for Ca, Mg and Na determinations.

Figure 2
Surface response obtained from the central composite design for C.

In general, a longer time allows better results in the sample decomposition process. When the decompositions were performed in less than 180 min, an incomplete decomposition was observed. The intermediate volume of 7.5 mL of HNO3 allowed us to obtain a clear solution, ready to be analyzed in MIP-OES. The ideal temperature was 160 °C, also ensuring the boiling point of the HNO3, which is approximately 120 °C and ensuring the breakdown of the bonds between the analyte and proteins in the case of Zn and Cu2929 Kpee, F.; Ozioma, E.; Ihunwo, L.; J. Appl. Sci. Environ. Manage.. 2009, 13, 63. or with lipids,3030 Lima, R. G. D. S.; Araújo, F. G.; Maia, M. F.; Pinto, A. S. D. S. B.; Environ. Res.. 2002, 89, 171. allowing the analytes to be free in solution. These conditions are confirmed by the study of C, where lower C concentrations were found under these conditions (trial 8 on Table S3, SI section).

Since no variables were statistically significant for Al, Cu, Fe, K and Zn, the same conditions of acid decomposition employed for Ca, Mg and Na were used in order to standardize the method. The accuracy of the method was evaluated with the use of standard reference material, as well as the addition and recovery test.

Analytical results

Figures of merit for the determination of the analytes Al, Ca, Cd, Cr, Cu, Fe, Hg, K, Mg, Na and Zn in chicken breast samples by MIP-OES were obtained from calibration curves data and the two sample introduction systems were used: conventional nebulization and MSIS (Tables S5 and S6, respectively, SI section).

The linear range for conventional nebulization was 0.5-5.0 mg L-1 and for multimode sample introduction system it was 10-250 μg L-1. For both systems, the calibration curves presented a linear correlation coefficient > 0.99, indicating good linearity. The limits of detection and quantification obtained are adequate for the determination of metals in chicken breast samples. The multimode system presented better values probably because the chemical generation of vapor occurs simultaneously with the nebulization. The generation of hydrogen, from the reducing agent, increases the plasma energy and consequently improves the emission for hydride and nonhydride-forming elements and the sensitivity, as can be observed by the angular coefficients values of the obtained curves.2020 Machado, R. C.; Amaral, C. D. B.; Nóbrega, J. A.; Nogueira, A. R. A.; J. Agric. Food Chem.. 2017, 65, 4839.

The limits of detection obtained using the conventional nebulization and considering the sample mass were lower those reported by Menezes et al.1515 Menezes, E. A.; Oliveira, A. F.; França, C. J.; Souza, G. B.; Nogueira, A. R. A.; Food Chem.. 2018, 240, 75. and Ogbomida et al.3131 Ogbomida, E. T.; Nakayama, S. M. M.; Bortey-Sam, N.; Oroszlany, B.; Tongo, I.; Enuneku, A. A.; Ozekeke, O.; Ainerua, M. O.; Fasipe, I. P.; Ezemonye, L. I.; Mizukawa, H.; Ikenaka,Y.; Ishizuka, M.; Ecotoxicol. Environ. Saf.. 2018, 151, 98. that determined the concentration of metals by ICP-OES in crude protein in beef, pork and chicken after microwave-assisted digestion and in tissue chicken by ICP-MS, respectively.

The accuracy of the method was evaluated using standard reference material with matrix similar to the samples and the results (considering the sample wet) are shown in Table 1. The results were submitted to the statistical test (t-test, 95% confidence level) and no significant differences between the results were observed, for both sample introduction systems. The recovery range for the conventional nebulization was between 94 to 103% (with good accuracy) and relative standard deviation value (RSD) lower than 8.6%, also attesting to a good precision. For the multimode system, the recovery range was 94 to 108% and RSDs were lower than 6.8%. Sodium could not be determined through the MSIS because sodium borohydride is introduced into the system during the analysis.

Table 1
Analytical results of the concentrations for Ca, Fe, K, Mg, Na and Zn in SRM 1546 using a conventional nebulization (CN) and multimode sample introduction system (MSIS)

For Al, Cd, Cr, Cu and Hg the accuracy was assessed through the addition and recovery test by adding three levels of the inorganic standards concentration to a chicken breast sample using both sample introduction system. All the samples were spiked prior to the decomposition procedure. In some cases, the concentrations of these analytes on SRM presented lower values than the first point of the calibration curve. The results are shown in Tables 2 and 3. The recoveries for conventional nebulization ranged from 80 to 108% and for MSIS ranged from 80 to 121% showing good accuracy. The precision was verified, and the values of RSDs were lower than 8.8%.

Table 2
Concentrations of Al, Cd, Cr, Cu and Hg measured by MIP-OES in conventional chicken breast sample after the additions of analytes using conventional nebulization
Table 3
Concentrations of Al, Cd, Cr, Cu and Hg measured by MIP-OES in conventional chicken breast sample after the additions of analytes using MSIS

After establishing the sample preparation method, breast from conventional chicken, country chicken, Christmas chicken and turkey were analyzed using the conventional nebulization and multimode sample introduction system. The obtained concentrations for Al, Cd, Cr, Cu, Fe, Hg, K, Mg, Na and Zn are shown in Table 4. The RSDs values were lower than 11.8%, confirming the good precision of analysis. The results were submitted to the Tukey’s test at the 95% confidence level, comparing similarity/difference between nebulization methods (column) or comparing element values in the same nebulization method for different samples (line).

Table 4
Concentrations obtained for Al, Ca, Cd, Cr, Cu, Fe, Hg, K, Mg, Na and Zn by MIP-OES in chicken breast sample using the conventional nebulization (CN) and multimode system (MS) (n = 3)

The knowledge about food composition is essential for quality control, for the assessment of essential nutrients intake and for the evaluation of exposure risks resulting from the metals ingestion. According to the results of the present study, the order of the elements found in the chicken breast was K > Na > Mg > Ca > Zn > Fe > Al > Cu. Concentrations of Cd, Cr and Hg were below the limit of quantification.

Among the investigated metals, the highest concentrations were found in the conventional chicken for Al, Ca, Cu, K and Mg. This may be due to the way of raising conventional chicken, if given by a greater anthropogenic action. For Zn, the highest concentrations were found in turkey breast sample. The highest Na values were found in the breast of turkey and Christmas chicken, because these samples were already spiced when purchased.

Andrade et al.3232 Andrade, E. C. B.; Barros, A. M.; Mello, V. S.; Takase, I.; Ciênc. Tecnol. Aliment.. 2004, 24, 393. evaluated the concentration of Cu and Zn in conventional chicken breast samples and found 0.48 and 0.76 mg kg-1 of Cu and Zn, respectively. These results were lower than those reported by Sun and Xing,3333 Sun, B.; Xing, M.; Biol. Trace Elem. Res.. 2016, 169, 359. which was 0.52 mg kg-1 for Cu and 7.06 mg kg-1 for Zn, but were close to the ones in the present study for Zn: 7.72 mg kg-1. In the same study, the concentration values found for Mg, Al, Na and K were 253.77; 3.27; 474.858 and 3,471.52 mg kg-1, respectively. These values are also close to the present study, which were 292.62; 2.77; 312.03 and 3,236.0 mg kg-1 for Mg, Al, Na and K, respectively.

For Hg and Cd, the found concentrations values were below the reference limit in muscle that is 30 μg kg-1 and 0.05 mg kg-1, respectively.3434 Ministério da Agricultura, Pecuária e Abastecimento (MAPA); Plano de Amostragem e Limites de Referência para o Plano Nacional de Controle de Resíduos e Contaminantes em Produtos de Origem Animal, Instrução Normativa No. 9/2017 de 21/02/2017, publicado em 08/03/2017, Diário Oficial da União (DOU): Brasília, 2017.,3535 Agência Nacional de Vigilância Sanitária (ANVISA); MERCOSUL/GMC, Regulamento Técnico Mercosul sobre Limites Máximos de Contaminantes Inorgânicos em Alimentos, Resolução No. 42/2013 de 29/08/2013, publicado em 30/08/2013, Diário Oficial da União (DOU): Brasília, 2013. The Brazilian legislation does not establish maximum levels for Cr.

Table 5 shows the recommended daily intake values3636 Food and Nutrition Board, Institute of Medicine; Dietary Reference Intakes for Vitamin A, Vitamin K, Arsenic, Boron, Chromium, Copper, Iodine, Iron, Manganese, Molybdenum, Nickel, Silicon, Vanadium, and Zinc; National Academy Press: Washington, DC, 2001. for the analytes Ca, Cu, Fe, K, Mg, Na, and Zn and the calculated values for conventional chicken, country chicken, turkey and Christmas chicken considering the recommended daily requirement of meat for an adult individual of 100 g per day.3636 Food and Nutrition Board, Institute of Medicine; Dietary Reference Intakes for Vitamin A, Vitamin K, Arsenic, Boron, Chromium, Copper, Iodine, Iron, Manganese, Molybdenum, Nickel, Silicon, Vanadium, and Zinc; National Academy Press: Washington, DC, 2001.

37 Agência Nacional de Vigilância Sanitária (ANVISA); Regulamento Técnico sobre Rotulagem Nutricional de Alimentos Embalado, Resolução No. 360 de 23/12/2003, publicado em 26/12/2003, Diário Oficial da União (DOU): Brasília, 2003.

38 Nakasato, M.; Rev. Bras. Hipertens.. 2004, 11, 95.
-3939 Food and Agriculture Organization, World Health Organization (FAO/OMS); Human Vitamin and Mineral Requirements, Report 7th Joint Expert Consultation; World Health Organization: Bangkok, Thailand, 2001. The calculated values for all samples are below the recommended daily intake limit for the investigated metals, which shows that chicken’s meat are a complementary part of a healthy diet and that there is a need for other sources providing the nutrients of these analytes, considered essential for the functioning of cellular metabolism. For Christmas chicken (spiced), Na presented a high intake value (403.60 mg per 100 g). For Al, the maximum limit allowed for all ages is 2 mg kg-1 of body weight.3636 Food and Nutrition Board, Institute of Medicine; Dietary Reference Intakes for Vitamin A, Vitamin K, Arsenic, Boron, Chromium, Copper, Iodine, Iron, Manganese, Molybdenum, Nickel, Silicon, Vanadium, and Zinc; National Academy Press: Washington, DC, 2001. The value obtained in the conventional chicken was 0.28 mg per 100 g, which is below the tolerable limit, demonstrating that there is no risk of intoxication by this element through the ingestion of this kind of food.

Table 5
Comparison between results of intake with recommended daily intake

Conclusions

From the results was possible to conclude that the sample preparation method employing the reflux system allows a suitable decomposition. We used only HNO3 for sample decomposition, simplifying the method and the results presented accuracy and precision. It was possible to determine the concentrations of Al, Ca, Cd, Cr, Cu, Fe, Hg, K, Mg, Na and Zn in the breast of conventional and country chicken, turkey and Christmas chicken samples by MIP-OES. Limits of detection obtained are suitable for the determination of metals in chicken breast samples. The highest analyte concentrations were obtained in the conventional chicken, the most exposed matrix to anthropogenic actions. The analytes presented concentrations lower than the recommended daily intake, showing that chicken breast should be a complementary part of a healthy diet.

Supplementary Information

Supplementary data are available free of charge at http://jbcs.sbq.org.br as PDF file.

Acknowledgments

The authors gratefully acknowledge the Conselho Nacional de Desenvolvimento Científico e Tecnológico (CNPq) for productivity scholarship (process No. 311575/2018-8). This study was financed in part by the Coordenação de Aperfeiçoamento de Pessoal de Nível Superior - Brasil (CAPES) Finance Code 001.

References

  • 1
    Brazilian Association of Animal Protein (ABPA); Brazilian Chicken; available at http://www.brazilianchicken.com.br/en and http://abpa-br.com.br/storage/files/relatorio-anual-2018.pdf accessed in June 2019.
    » http://www.brazilianchicken.com.br/en and http://abpa-br.com.br/storage/files/relatorio-anual-2018.pdf
  • 2
    Empresa Brasileira de Pesquisa Agropecuária (EMBRAPA); Embrapa Suínos e Aves; available at https://www.embrapa.br/suinos-e-aves accessed in June 2019.
    » https://www.embrapa.br/suinos-e-aves
  • 3
    Pereira, T. E. J.; Ströher, G. R.; Turbiani, F. R. B.; Braz. J. Food Technol. 2013, 16, 278.
  • 4
    Bohrer, B. M.; Trends Food Sci. Technol. 2017, 65, 103.
  • 5
    United States Department of Agriculture (USDA); https://ndb.nal.usda.gov/ndb/ accessed in June 2019.
    » https://ndb.nal.usda.gov/ndb/
  • 6
    Milicevic, D.; Trbovic, D.; Petrovic, Z.; Jakovac-Strajn, B.; Nastasijevic, I.; Koricanac, V.; Proc. Food Sci. 2015, 5, 191.
  • 7
    Chen, S.; Lin, Y.; Kao, Y.; Shih, Y.; Food Addit. Contam., Part B 2013, 6, 231.
  • 8
    da Silva, D. C. F.; de Arruda, A. M. V.; Gonçalves, A. A.; J. Food Sci. Technol. 2017, 54, 1818.
  • 9
    Cabrera, M. C.; Ramos, A.; Saadoun, A.; Brito, G.; Meat Sci. 2010, 84, 518.
  • 10
    Hunter, P.; Eur. Mol. Biol. Organ 2008, 9, 15.
  • 11
    Zeng, H.; Uthus, E. O.; Combs, G. F.; Inorg. Biochem. 2005, 99, 1269.
  • 12
    Uluozlu, O. D.; Tuzena, M.; Mendil, D.; Soylak, M.; J. Hazard. Mater. 2009, 163, 982.
  • 13
    Celik, U.; Oehlenschlager, J.; Food Control 2007, 18, 258.
  • 14
    Hu, Y.; Zhang, W.; Chen, G.; Cheng, H.; Tao, S.; Environ. Pollut. 2018, 234, 667.
  • 15
    Menezes, E. A.; Oliveira, A. F.; França, C. J.; Souza, G. B.; Nogueira, A. R. A.; Food Chem. 2018, 240, 75.
  • 16
    Wu, Y.; Zhanh, H.; Liu, G.; Zhang, J.; Wang, J.; Yu, Y.; Lu, S.; Chemosphere 2016, 144, 564.
  • 17
    Ríos, S. E. G.; Peñuela, G. A.; Botero, C. M. R.; Food Anal. Methods 2017, 10, 3407.
  • 18
    de Souza, A. O.; Pereira, C. C.; Heling, A. I.; Oreste, E. Q.; Cadore, S.; Vieira, M. A.; Ribeiro, A. S.; J. Food Compos. Anal. 2019, 77, 60.
  • 19
    Matusiewicz, H.; Slachcinski, M.; J. Braz. Chem. Soc. 2016, 27, 584.
  • 20
    Machado, R. C.; Amaral, C. D. B.; Nóbrega, J. A.; Nogueira, A. R. A.; J. Agric. Food Chem. 2017, 65, 4839.
  • 21
    Oreste, E. Q.; de Jesus, A.; de Oliveira, R. M.; da Silva, M. M.; Vieira, M. A.; Ribeiro, A. S.; Microchem. J. 2013, 109, 5.
  • 22
    de Oliveira, R. M.; Antunes, A. C. N.; Vieira, M. A.; Medina, A. L.; Ribeiro, A. S.; Microchem. J. 2016, 124, 402.
  • 23
    Pereira, C. C.; de Souza, A. O.; Oreste, E. Q.; Cidade, M. J. A.; Cadore, S.; Ribeiro, A. S.; Vieira, M. A.; J. Braz. Chem. Soc. 2016, 27, 685.
  • 24
    Oreste, E. Q.; de Souza, A. O.; Pereira, C. C.; Lisboa, M. T.; Cidade, M. J. A.; Vieira, M. A.; Cadore, S.; Ribeiro, A. S.; Food Anal. Methods 2015, 9, 777.
  • 25
    Gouveia, S. T.; Silva, F. V.; Costa, L. M.; Nogueira, A. R. A.; Nóbrega, J. A.; Anal. Chim. Acta 2001, 445, 269.
  • 26
    Statistica 7.0 software; Statsoft Inc., Tulsa, OK, USA, 2004.
  • 27
    Instituto Nacional de Metrologia, Qualidade e Tecnologia (INMETRO); Orientação sobre Validação de Métodos de Ensaios Químicos, DOQ-CGCRE-008, rev. 2; INMETRO: Rio de Janeiro, 2007, p. 14.
  • 28
    OriginPro v8.0724; OriginLab, Northampton, USA, 2007.
  • 29
    Kpee, F.; Ozioma, E.; Ihunwo, L.; J. Appl. Sci. Environ. Manage. 2009, 13, 63.
  • 30
    Lima, R. G. D. S.; Araújo, F. G.; Maia, M. F.; Pinto, A. S. D. S. B.; Environ. Res. 2002, 89, 171.
  • 31
    Ogbomida, E. T.; Nakayama, S. M. M.; Bortey-Sam, N.; Oroszlany, B.; Tongo, I.; Enuneku, A. A.; Ozekeke, O.; Ainerua, M. O.; Fasipe, I. P.; Ezemonye, L. I.; Mizukawa, H.; Ikenaka,Y.; Ishizuka, M.; Ecotoxicol. Environ. Saf. 2018, 151, 98.
  • 32
    Andrade, E. C. B.; Barros, A. M.; Mello, V. S.; Takase, I.; Ciênc. Tecnol. Aliment. 2004, 24, 393.
  • 33
    Sun, B.; Xing, M.; Biol. Trace Elem. Res. 2016, 169, 359.
  • 34
    Ministério da Agricultura, Pecuária e Abastecimento (MAPA); Plano de Amostragem e Limites de Referência para o Plano Nacional de Controle de Resíduos e Contaminantes em Produtos de Origem Animal, Instrução Normativa No. 9/2017 de 21/02/2017, publicado em 08/03/2017, Diário Oficial da União (DOU): Brasília, 2017.
  • 35
    Agência Nacional de Vigilância Sanitária (ANVISA); MERCOSUL/GMC, Regulamento Técnico Mercosul sobre Limites Máximos de Contaminantes Inorgânicos em Alimentos, Resolução No. 42/2013 de 29/08/2013, publicado em 30/08/2013, Diário Oficial da União (DOU): Brasília, 2013.
  • 36
    Food and Nutrition Board, Institute of Medicine; Dietary Reference Intakes for Vitamin A, Vitamin K, Arsenic, Boron, Chromium, Copper, Iodine, Iron, Manganese, Molybdenum, Nickel, Silicon, Vanadium, and Zinc; National Academy Press: Washington, DC, 2001.
  • 37
    Agência Nacional de Vigilância Sanitária (ANVISA); Regulamento Técnico sobre Rotulagem Nutricional de Alimentos Embalado, Resolução No. 360 de 23/12/2003, publicado em 26/12/2003, Diário Oficial da União (DOU): Brasília, 2003.
  • 38
    Nakasato, M.; Rev. Bras. Hipertens. 2004, 11, 95.
  • 39
    Food and Agriculture Organization, World Health Organization (FAO/OMS); Human Vitamin and Mineral Requirements, Report 7th Joint Expert Consultation; World Health Organization: Bangkok, Thailand, 2001.

Publication Dates

  • Publication in this collection
    24 Oct 2019
  • Date of issue
    Nov 2019

History

  • Received
    14 Feb 2019
  • Accepted
    2 July 2019
Sociedade Brasileira de Química Instituto de Química - UNICAMP, Caixa Postal 6154, 13083-970 Campinas SP - Brazil, Tel./FAX.: +55 19 3521-3151 - São Paulo - SP - Brazil
E-mail: office@jbcs.sbq.org.br