Evelina Fasano

Children's exposure to Di(2-ethylhexyl)phthalate and dibutylphthalate plasticizers from school meals.

Packed school meals for children 3-10 years old were studied to evaluate the levels of di(2-ethylhexyl)phthalate (DEHP) and di-n-butylphthalate (DBP) and the influence of the packaging process on meal contamination, and their contribution to daily intake was estimated. The packaging consisted of polyethylene-coated aluminum (PE/Al) dishes thermally welded by a polyethyleneterephthalate-coated aluminum (PET/Al) foil. Foodstuffs before processing were analyzed, too. Total meals before packaging and after packaging were collected. It was found that 92% of foodstuffs employed in meal preparation contained DEHP, and 76% of them DBP, at detectable levels. In cooked foods before packaging the DEHP median concentration levels varied from 111.4 to 154.8 ng/g ww and those of DBP between 32.5 and 59.5 ng/g ww. In packed meals the DEHP median values ranged from 127.0 to 253.3 ng/g ww, and DBP median values varied from 44.1 to 80.5 ng/g ww. The mean increases of median concentrations of DEHP in cooked foods before and after packaging were 113 and 125% for DBP. For nursery and primary school children DEHP intake via school meals can raise on average the respective EFSA TDI by 18 and 12% and that of DBP by 50 and 30%.

Survey of lead, cadmium, mercury and arsenic in seafood purchased in Campania, Italy

Lead, cadmium, mercury and arsenic were surveyed in fresh catch, farmed and frozen marine fish, cephalopods and mussels marketed in Campania (Italy), and the populations weekly intake from seafood was assessed. A total of 162 specimens of fish and cephalopods and 30 pools of mussels were analyzed. Pb levels in fresh catch species ranged between <20 and 689 ng/g; in farmed from <20 to 438 ng/g and in frozen from <20 to 541 ng/g. Cd values ranged in fresh catch seafood from <0.8 to 19.8 ng/g; in farmed from <0.8 to 42.3 ng/g; in frozen from <0.8 to 93.1. Hg levels ranged 8–339 ng/g in wild seafood; <5–226 ng/g in farmed and <5–313 ng/g in frozen. In fresh catch seafood, As values ranged <10–231 ng/g; in farmed from 12–310 ng/g and in frozen 12–272 ng/g. Cd and Hg concentrations were below the EU limits in all species; two samples of farmed European seabass and two frozen samples exceeded EU limits for Pb. The median weekly dietary intake could affect the provisional tolerable weekly intake (PTWI) of Pb by 2% (range 0.5–16.5%), Cd PTWI by 0.9% (range 0.1–8.0%), Hg PTWI by 9.6% (range 0.6–41.0%) and the As PTWI by 3.6% (range 0.4–12.5%). Considering the upper values in the ranges, seafood represents a non-negligible contribution to Pb weekly intake (16.5%), but mainly to the weekly intake of Hg (41.0%) for high seafood consumers and those consuming the most contaminated species.

Exposure to Di-2-Ethylhexyl Phthalate, Di-N-Butyl Phthalate and Bisphenol A through Infant Formulas

Phthalates and bisphenol A (BPA) are ubiquitous contaminants identified as endocrine disruptors. Phthalates are worldwide used as plasticizers, in particular to improve the mechanical properties of polymers such as polyvinyl chloride. Because they are not chemically bound to the polymer, they tend to leach out with time and use. Di-2-ethylhexyl phthalate (DEHP) and di-n-butyl phthalate (DnBP) are the two most common phthalates. BPA is an estrogenic compound used to manufacture polycarbonate containers for food and drink, including baby bottles. It can migrate from container into foods, especially at elevated temperatures. Diet is a predominant source of exposure for phthalates and BPA, especially for infants. The aim of this study was to test the presence of DEHP, DnBP, and BPA in infant formulas. DEHP, DnBP, and BPA concentrations were measured in 22 liquid and 28 powder milks by gas chromatography with flame ionization detection and high performance liquid chromatography with fluorimetric detection, respectively. DEHP concentrations in our samples were between 0.005 and 5.088 μg/g (median 0.906 μg/g), DnBP concentrations were between 0.008 and 1.297 μg/g (median 0.053 μg/g), and BPA concentrations were between 0.003 and 0.375 μg/g (median 0.015 μg/g). Concentrations of the investigated contaminants in liquid and powder milks were not significantly different, even though samples were packed in different types of containers. These data point out potential hazards for infants fed with baby formulas. Contamination seems more related to the production of formulas than to a release from containers.

Determination of BPA, BPB, BPF, BADGE and BFDGE in canned energy drinks by molecularly imprinted polymer cleaning up and UPLC with fluorescence detection.

A new method for simultaneous determination of five bisphenols in canned energy drinks by UPLC with fluorescence detection, after clean up on molecularly imprinted polymers, is herein described. The method was validated at two concentration levels, calculating trueness, repeatability and within-laboratory reproducibility, specificity, linearity of detector response, the limits of quantifications and the limits of detection for each bisphenol. The method is specific, reliable and very sensitive, allowing for determination of bisphenol F diglycidyl ether (BFDGE), bisphenol A (BPA), bisphenol B (BPB), bisphenol F (BPF) and bisphenol A diglycidyl ether (BADGE) down to 0.50ng/mL; it was employed to determine contamination levels from these bisphenols in forty energy drinks of different brands, collected from the market in Naples. BPA was detected in 17 out of 40 samples (42.5%); in some energy drinks also BPF, BADGE and BFDGE were determined.

Di(2-ethylhexyl)phthalate (DEHP) and di-n-butylphthalate (DBP) exposure through diet in hospital patients

Ready-to-eat packed meals intended to hospital patients were studied over a two-weeks period to measure the contents of di-(2-ethylhexyl) phthalate (DEHP) and di-n-butylphthalate (DBP) and to evaluate their daily intake by total diet. The packaging consisted of polyethylene terephthalate (PET) dishes sealed with polypropylene (PP) foil. The DEHP mean concentrations in total meals varied from 0.061±0.028 to 0.307±0.138μg/gwetweight (wet wt.); the DBP mean levels varied from 0.025±0.018 to 0.174±0.091μg/gwetwt. Highest levels of concentration for DEHP and DBP were found in bread with mean values of 0.307±0.138μg/gwetwt. and 0.174±0.091μg/gwetwt. for DEHP and DBP, respectively. The daily intake for DEHP was 3.1±0.9μg/kgbw and 1.5±0.5μg/kgbw for DBP. The mean±sd incidence of DEHP and DBP intake via hospital meals on the respective EFSA TDI was 6±2% (range 4-11%), and 15±5% (range 8-24%), respectively. Even if for hospital patients the major route of exposure may be represented by medical devices, the influence of the diet could have a significant value on TDI.

Study on the influence of temperature, storage time and packaging type on di-n-butylphthalate and di(2-ethylhexyl)phthalate release into packed meals

Ready-to-eat meals packed in polyethylene terephthalate (PET) and aluminium dishes, supplied to patients in two hospitals in the Campania region (Italy), were studied to evaluate the probable migration of di-n-butylphthalate (DBP) and di(2-ethylhexyl)phthalate (DEHP) from the packaging into the food. The influence of temperature, storage time and type of package on the migration process was considered, analysing the meals according to three time ranges, before the packaging (T 0) and after 60 min (T 1) and 120 min (T 2) from packaging during the storage in thermostatic delivery carts. At T 0 in the meals sampled before packaging in PET dishes, mean levels of DBP and DEHP were 0.023 ± 0.002 µg/g and 0.069 ± 0.041 µg/g, respectively; the DBP level increased 230% and that of DEHP increased 208% by time T 0 versus T 2. In the meals sampled before packaging (T 0) in aluminium dishes, the mean levels of DBP and DEHP were 0.030 ± 0.001 µg/g and 0.057 ± 0.015 µg/g, respectively. The significant increase in contaminant levels over storage times for meals packed in PET dishes demonstrates that from packages made of plastic materials the migration of phthalic acid esters into foods is possible. In meals packed in PET dishes, the highest DBP and DEHP increases were observed in the T 0 to T 1 range, which represented the time interval over which meals were kept hot, and mainly in the first ones, where the highest temperatures have been recorded.

Assessment of the dietary habits and polycyclic aromatic hydrocarbon exposure in primary school children

Thirty Italian children, 7–9 year aged, living in Naples were investigated on their dietary habits and on polycyclic aromatic hydrocarbon (PAH) exposure by a food diary-questionnaire and one week duplicate diet sample analyses. Daily total food consumption mean value was 632 ± 215 g day−1, median value 613 g day−1. The daily energy intake and the diet composition meanly agreed with the official guidelines for the Italian children. Sixteen PAHs were simultaneously detected and, according to the European Food Safety Authority (EFSA) approach, benzo[a]pyrene; benzo[a]pyrene + chrysene (PAH2); PAH2 + benz[a]anthracene + benzo[b]fluoranthene (PAH4); PAH4 + benzo[k]fluoranthene + benzo[ghi]perylene + dibenz[a, h]anthracene + indeno[1,2,3-cd]pyrene (PAH8) were considered in evaluating the childrens dietary exposure to PAHs. The benzo[a]pyrene (BaP) median concentrations in foods varied from 0.06 to 0.33 µg kg−1. Only three samples of cooked foods (one fish and two meat samples) exceeded legal limits fixed by the European Union for BaP. Daily median intakes of benzo[a]pyrene, PAH2, PAH4, and PAH8 were 153; 318; 990; 1776 ng day−1; their median exposure values were 5; 10; 28; 54 ng kg−1 bw day−1. The Margins of Exposure (MOEs) in median consumers agreed with the EFSA safety values except for PAH8.

Detection of polycyclic aromatic hydrocarbons in smoked buffalo mozzarella cheese produced in Campania Region, Italy.

BACKGROUND Smoked mozzarella is obtained through traditional smoking techniques or the use of liquid smoke. Polycyclic aromatic hydrocarbons (PAHs) may be produced during the organic matrix combustion. The aim of this study was to evaluate benzo[a]pyrene (B(a)P), benzo[a]anthracene (B(a)A), benzo[b]fluoranthene (B(b)FA), benzo[k]fluoranthene (B(k)FA), benzo[ghi]perylene (B(g,h,i)PE), chrysene (CHR), dibenz[a,h]anthracene (DB(a,h)A) and indeno[1,2,3-cd]pyrene (IP) in smoked buffalo mozzarella produced in Campania, evaluating also the influence of the different smoking techniques. Milk and mozzarella of the same batch, before and after smoking, were collected. The detection method was basic hydrolysis, clean-up with silica and detection by HPLC equipped with a fluorescence detector. RESULTS For milk, only 30% was contaminated. In non-smoked products the medians were >LODs only for B(a)A and CHR. In smoked mozzarellas the highest median was 0.37 ng g(-1) wet weight (CHR). CONCLUSION It was found that the consumption of this typical food of Campania does not represent a risk for consumers, considering that the incidences on EFSA dietary intake were always lower than 1.5% for mozzarella cheese and lower than 3% for smoked mozzarella cheese.

Determination of acrylamide levels in potato crisps and other snacks and exposure risk assessment through a Margin of Exposure approach

Potato crisps, corn-based extruded snacks and other savoury snacks are very popular products especially among younger generations. These products could be a potential source of acrylamide (AA), a toxic compound which could develop during frying and baking processes. The purpose of this study was the assessment of the dietary intake to AA across six groups of consumers divided according to age through the consumption of potato crisps and other snacks, in order to eventually evaluate the margin of exposure (MOE) related to neurotoxic and carcinogenic critical endpoints. Different brands of potato crisps and other popular snacks were analyzed through a matrix solid-phase dispersion method followed by a bromination step and GC-MS quantification. The concentration of detected AA ranged from 21 to 3444 ng g-1 and the highest level occurred in potato crisps samples which showed a median value of 968 ng g-1. The risk characterization through MOE assessment revealed that five out of six consumers groups showed higher exposure values associated with an augmented carcinogenic risk.

Bisphenol A contamination in soft drinks as a risk for children’s health in Italy

Bisphenol A (BPA) was determined in sugary carbonated, non-carbonated and milk-based beverages, through HLPC-fluorescence detection and confirmed by LC-MS/MS, in a selection of brands that are mostly consumed by Italian children. The daily intake was determined through the WHO budget method (BM). BPA was found at detectable levels in 57% of carbonated beverages, in 50% of non-carbonated and in 100% of milk-based beverages. The median concentrations were 1.24 µg l–1 (range = < LOD–4.98 µg l–1) in canned carbonated beverages and 0.18 µg l–1 (< LOD–1.78 µg l–1) in non-canned carbonated beverages. In non-carbonated beverages, median concentrations were 0.80 µg l–1 (< LOD–2.79 µg l–1) and 0.18 µg l–1 (< LOD–3.58 µg l–1), respectively, for canned and non-canned beverages; in milk-based products the BPA median concentration was 3.60 µg l–1 (1.00–17.65 µg l–1). BPA daily intake from sugary drink consumption in children ranged from 0.008 to 1.765 µg kg–1 bw day–1. The median exposure values for the ‘best’ and ‘worst’ cases were 0.16% and 0.47% respectively of the EFSA t-TDI for BPA (4 µg kg–1 bw day–1), and 10.59% and 35.30% of the t-TDI when the maximum levels were considered.