Lead, cadmium, mercury and arsenic were surveyed in fresh catch, farmed and frozen marine fish, cephalopods and mussels marketed in Campania (Italy), and the population's 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.
We evaluated the concentration and congener distribution of seven "target" polychlorinated biphenyls (PCBs) present in water collected in different aquaculture farms of the Mediterranean area, commercial feeds, and farmed seafood. PCBs were present in feed and in tissues of all the analysed organisms at levels ranging from 1.96 ng g(-1) to 124.00 ng g(-1) wet weight, and in 10.5% of the water samples, at levels from under detection limit to 33.0 ng l(-1) with total PCB concentrations significantly higher in samples from the Tyrrhenian Sea than the Adriatic Sea. PCB congener distribution in tissues resembled that of feed, suggesting that commercial feed is an important source of PCBs. The estrogenicity of organic extracts of the samples was also evaluated by using an in vitro yeast reporter assay. Estrogenic activity higher than 10% of the activity induced by 10 nM 17 beta-estradiol was observed in 20.0% of seafood samples and 15.8% of water samples. Seafood and water samples from the Tyrrhenian Sea were more frequently estrogenic than the Adriatic ones (16.45 versus 4.08%). A significant correlation of total PCB concentrations on biological activity was observed for sea bass and mussels from the Adriatic Sea (p < 0.045 and p < 0.04, respectively), and for sea bass of the Tyrrhenian Sea (p = 0.05). These results indicate the need of an integral approach in the exposure assessment to potential toxic compounds for human via food.
Multipathway exposure to polycyclic aromatic hydrocarbons (PAHs) and Pyrene (Py) was studied among children ages 7-9 living in two areas of the Campania Region (South-Italy) classified as urban and rural. During five consecutive days PAHs and Py were detected in air samples from outdoors, indoors (school and home), individuals at inhalatory levels, and in food and beverages (defined as food) consumed daily by each child. 1-hydroxypyrene (1-OHP) was detected in children's urine. Gender, weight and height of each subject were recorded, and the personal Body Mass Index (BMI) calculated. The type of home heating, the presence of smokers and the number of cigarettes smoked at home was determined. Total PAH and Py median concentrations in outdoor air from urban areas were 1.70 ng m(-3) and 0.19 ng m(-3), respectively while in rural areas they were 1.10 ng m(-3) and 0.14 ng m(-3). Indoor air total PAH and Py median concentrations were 2.50 ng m(-3) and 0.15 ng m(-3), respectively for urban areas, and 4.10 ng m(-3) and 0.15 ng m(-3) for rural areas. In food the total PAH and Py median levels were 10.44 and 0.81 microg kg(-1) in urban areas and 18.90 and 0.90 microg kg(-1) in rural areas. The median urinary levels of 1-OHP for urban and rural children were 0.07 and 0.06 micromol/mol creat., respectively. From these data, food appears to be the most relevant source of exposure to PAHs and Py. The Py intake from single (food or air) or total (food and air) pathways did not significantly correlate with the urinary 1-OHP excreted daily for each child during all 5 days of observation.
The urinary benzene metabolite trans,trans-muconic acid (MA) was determined in 144 children living in Campania (Italy): 92 from Naples (1,300,000 inhabitants), designated as an urban source, and compared to 52 from Pollica (300 inhabitants), considered a rural, background exposure for benzene. The children participating in the study were tested by an anonymous questionnaire about the possible sources of exposure to benzene. Quantifiable levels of MA were found in 63% of the urine samples analyzed. Setting the value of nondetectable urinary samples at 7 microg/L MA, a value that is one-half of the instrument detection limit of 14 microg/L, the mean urinary concentration levels were 98.7+/-81.0 microg/L and 48.4+/-71.7 microg/L in Naples and Pollica, respectively; adjustment of these values to creatinine clearance resulted in MA levels of 141.2+/-145.4 microg/L in Naples and 109.8+/-133.2 microg/L in Pollica. Passive smoke exposure did not significantly affect urinary MA levels, but proximity of the home to traffic increased urine MA content. Data show that MA can be utilized as a biomarker for exposure; however, a clear-cut association to benzene requires personal monitoring and control of dietary sorbic acid.
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