Abstract:This Research Communication reports analysis of 37 compounds comprising polycyclic aromatic hydrocarbons (PAHs), organochlorine and organophosphate pesticides (OCPS and OPPS) in milk powder (one brand each of commercial infant formulae, follow-on formulae and baby formulae purchased from a local supermarket in Romania). The selected analytes were investigated using gas chromatography-mass spectrometry (GC-MS), gas chromatography with electron capture detector (GC-ECD) and gas chromatography with thermionic sen… Show more
“…e extraction of PAHs in infant formula powders includes direct saponification [1,2,23], solvent extraction [22,25,26], and dispersive solid phase extraction, and a simplified version of conventional method named the quick, easy, cheap, effective, rugged, and safe (QuEChERS) extraction method has been used for the multiresidue analysis. e analytical method for the determination of the US EPA priority pollutant of 16 PAHs in edible oils was developed by an isotope dilution GC-MS method [27], which is a reference for this study, and all parameters are listed in Figure 1.…”
A gas chromatography-mass spectroscopy (GC-MS) method was developed to assess the infant exposure assessment from four important polycyclic aromatic hydrocarbon (PAH) markers in infant formula powder: benzo[a]anthracene, chrysene, benzo [b] fluoranthene, and benzo[a]pyrene (collectively referred to as PAH4). e developed method required the addition of an isotopically labeled internal standard, sample extraction under alkali conditions, a saponification step, and a solid-phase extraction purification step. In a controlled spike test, the average recovery rates of PAH4 were 77.3% to 111.8% and the relative standard deviations were 4.8% to 14.2% (n = 6). e quantitative limit (LOQ) and detection limit (LOD) of the method were 0.5 and 0.1 μg·kg − 1 , respectively. e PAH4 content was analyzed in 30 commercially available infant formula powders. e PAH4 content was found to be in the range of 0.1 to 0.87 μg·kg − 1 . Combined with the daily intake of infant milk powder in China, the average and maximum daily exposure of BaP for stage-1 infants in China are 0.45 ng/kg.bw.d − 1 and 1.9 ng/kg.bw.d − 1 and the PAH4 values are 8.6 ng/kg.bw.d − 1 and 18.6 ng/kg.bw.d − 1 , respectively. e PAH4 content in the tested infant formula powders sold in the China were sufficiently low, and all of the tested products were safe for consumption.
“…e extraction of PAHs in infant formula powders includes direct saponification [1,2,23], solvent extraction [22,25,26], and dispersive solid phase extraction, and a simplified version of conventional method named the quick, easy, cheap, effective, rugged, and safe (QuEChERS) extraction method has been used for the multiresidue analysis. e analytical method for the determination of the US EPA priority pollutant of 16 PAHs in edible oils was developed by an isotope dilution GC-MS method [27], which is a reference for this study, and all parameters are listed in Figure 1.…”
A gas chromatography-mass spectroscopy (GC-MS) method was developed to assess the infant exposure assessment from four important polycyclic aromatic hydrocarbon (PAH) markers in infant formula powder: benzo[a]anthracene, chrysene, benzo [b] fluoranthene, and benzo[a]pyrene (collectively referred to as PAH4). e developed method required the addition of an isotopically labeled internal standard, sample extraction under alkali conditions, a saponification step, and a solid-phase extraction purification step. In a controlled spike test, the average recovery rates of PAH4 were 77.3% to 111.8% and the relative standard deviations were 4.8% to 14.2% (n = 6). e quantitative limit (LOQ) and detection limit (LOD) of the method were 0.5 and 0.1 μg·kg − 1 , respectively. e PAH4 content was analyzed in 30 commercially available infant formula powders. e PAH4 content was found to be in the range of 0.1 to 0.87 μg·kg − 1 . Combined with the daily intake of infant milk powder in China, the average and maximum daily exposure of BaP for stage-1 infants in China are 0.45 ng/kg.bw.d − 1 and 1.9 ng/kg.bw.d − 1 and the PAH4 values are 8.6 ng/kg.bw.d − 1 and 18.6 ng/kg.bw.d − 1 , respectively. e PAH4 content in the tested infant formula powders sold in the China were sufficiently low, and all of the tested products were safe for consumption.
“…Only two of the analyzed samples (3 M and 14 M) contained seven of carcinogenic PAHs at a mean concentration (0.46 µg/g) that is higher than the accepted range set by EPA [6].…”
Section: Resultsmentioning
confidence: 75%
“…In addition, the lipophilicity of PAHs results in their accumulation in animal adipose tissue and excretion in milk [6]. Milk and dairy products are the main components of the daily diet of humans and it is also of special importance as it can act as a complete food source [7].…”
In a market-basket study conducted in Cairo, Egypt, the most commonly consumed milk products were sampled and the contents of 13 polycyclic aromatic hydrocarbons were analyzed using gas chromatography with a mass spectrometer detector. The obtained data showed that the total amount of 13 PAHs was within the range of 1.3–8.2 µg/g. The results proved that the, highest mean levels of polycyclic aromatic hydrocarbons were detected in powdered milk (8.2 μg/g) followed by ultra-heat treatment milk and milk beverages (6.07 μg/g). The lowest level was detected in unsmoked cheese and yogurt (1.3 μg/g). Estimated daily intake (EDI) was used to estimate the carcinogenic risk. The total mean estimated daily intake for children in different age categories (1–10 years) was calculated with respect to benzo[a]pyrene, which ranged from 0.058 to 0.31 mg/day. The total mean value of EDI for the sum of seven carcinogenic PAHs in terms of benzo[a]pyrene ranged from 0.61 to 1.22 mg/day in all age categories. These results were higher than the critical limit set by the European Food Safety Authority. Therefore, there should be concerns regarding the effects of the consumption of different milk products on the local population.
“…No existe un método oficial para la determinación de HAP en leche, existiendo dos tendencias en la identificación y cuantificación de los mismos: 1) por cromatografía gaseosa empleando detector de ionización de flama y espectrometría de masas (15,16) , 2) por cromatografía de líquidos de alta resolución con detector de fluorescencia (7,8,17) . Para obtener mejores resultados en la preparación de las muestras se han empleado diferentes procedimientos que incluyen saponificación, extracción líquido-líquido (LLE) y limpieza por cromatografía en columna o más recientemente, extracción en fase sólida (SPE) (18,19,20) .…”
En la actualidad la presencia de hidrocarburos aromáticos policíclicos (HAP) en la leche se reconoce como contaminantes emergentes, por el efecto que pueden provocar en la salud humana. La identificación y cuantificación de estos requiere métodos analíticos que permitan una mayor estimación, por ello el objetivo del presente trabajo fue determinar la presencia de estos compuestos en marcas de leche evaluando tres procedimientos de extracción. Los HAPs por analizar fueron los 16 considerados como prioritarios por la Agencia de Protección del Medio Ambiente de los Estados Unidos. Se utilizaron cuatro marcas comerciales de leche entera (tres de leche ultrapasteurizada (UHT) y una de leche pasteurizada (HTST)), cada marca tuvo tres muestreos para una n= 12. El muestreo se realizó en el periodo marzo-junio de 2016. Los procedimientos de extracción fueron: saponificación de la leche (variante A), extracción por solución detergente (variante B) y extracción líquida-líquida (variante C); los procedimientos se analizaron por cromatografía de gases con detector de ionización de flama. El 75 % de las muestras fueron positivas a por lo menos uno de los 16 HAP analizados. Los procedimientos de extracción presentaron diferencias entre variantes, la variante A únicamente identificó compuestos de bajo peso molecular (BPM), por su parte, la variante B identificó compuestos de alto peso molecular (APM) y BPM; sin embargo, los resultados muestran que la variante C presentó mejores porcentajes de recuperación (58.7±12.3 y 81.8±8.0) para HAP de alto y bajo peso molecular que la variante B (15.0±8.0 y 58.0±21.0) respectivamente.
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