The aim of the present study was to determine the levels of ochratoxin A (OTA) in pigs experimentally exposed to this mycotoxin and to evaluate if bile may be used to assess exposure to OTA. Twelve hybrid pigs were divided into 3 equal groups, a control group D0, and 2 experimental groups, D1 fed with 50 µg OTA/kg diet, and D2 fed with 500 µg OTA/kg diet for 15 days. At the end of the test, the animals were euthanized and samples of different tissues and biological fluids were analysed by HPLC-fluorescence detection for the presence of OTA. Samples of unconventional edible tissues such as lung and heart were also taken for analysis because they are used in typical Italian regional dishes. The Italian guidance value for OTA of 1 µg/kg established for pork meat and derived products has been exceeded in all the matrices from both the experimental groups. The comparison between OTA levels detected in D1 and D2 groups showed clearly a linear dose-response relationship. Based on the mean values measured, OTA distribution follows the order blood plasma > lung > kidney (in D1 group), heart (in D2 group) > heart (in D1 group), kidney (in D2 group) > bile > liver > fat > muscle. Analysis of bile can be useful for the detection of OTA in pigs. However, since blood can easily be taken from pigs, and given the correlation between the mycotoxin concentration detected in this matrix and the concentrations detected in the others, OTA level in blood is a more viable approach to assessing the presence of OTA in edible tissues. As lung and heart may contain high concentrations of OTA, the analytical controls should also include these matrices.
The occurrence of pesticides intended for non-agricultural use was investigated in 206 dust samples drawn from vacuum-cleaner bags from residential flats in Italy. The multi-residue analysis targeted on 95 different active principles was performed with UPLC-MS/MS, with a Limit of Quantification (LOQ) of 0.008 μg/g dry weight. The results indicated the presence of imidacloprid (IMI) and carbendazim (CARB) in 30% and 26% of the samples, with a mean and P95 concentration between 1.6 and 39 and between 0.08 and 4.9 μg/g, respectively. Combined presence of two biocides was noted in 19.4% samples, of three biocides in 9.2% samples, of four biocides in 3.4% samples, and of five and six biocides in 0.5% and 1% samples, respectively. According to the estimated dust intake in infants/toddlers aged 6-24 months (16-100 mg d) and cats (200 mg d), it was possible to obtain risk characterization with respect to the Acceptable Daily Intake (ADI) for IMI of 0.060 mg/kg body weight (bw) proposed by the European Food Safety Authority (EFSA) and the chronic Population Adjusted Dose (cPAD) of 0.019 mg/kg bw d by US-EPA. Under the worst-case scenario, the presence of IMI in dust indicates potential exceedance of the cPAD in kittens, to be considered as sentinel also accounting for combined exposure. This study highlights the relevance of consumer empowerment about the responsible use of pesticides as biocidal products in indoor environment.
In the present study, 58 samples of milk were analyzed for the presence of aflatoxin M (AFM). The samples were purchased during the period April-May 2013 in a random manner from local stores (supermarkets, small retail shops, small groceries, and specialized suppliers) located in the surrounding of Bologna (Italy). The commercial samples of milk were either organic (n = 22) or conventional (n = 36); fresh milk samples and UHT milk samples, whole milk samples, and partially skim milk samples were present in both the two considered categories. For the quantification of AFM in milk, the extraction-purification technique based on the use of immunoaffinity columns was adopted and analyses were performed using HPLC-FD. AFM was detected in 35 samples, 11 from organic production and 24 from conventional production. No statistically (P > 0.05) significant differences were observed in the concentration of AFM in the two categories of product. The levels of contamination found in the positive samples ranged between 0.009 and 0.026 ng mL. No sample exceeded the limit defined at community level for AFM in milk (0.05 μg kg). This demonstrates the effectiveness of the checks before the placing on the market of these food products. Thus, the "aflatoxins" problem that characterized the summer of 2012 does not seem to have had effect on the contamination level of the considered milk samples.
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