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Background. One of the important source of food contamination with elements harmful to human health such as lead or cadmium is migration from the articles intended to come into contact with food. Ceramic and glass articles can also be a source of zinc and copper which compounds are used during the production process of vessels. Objective. Determination of migration of lead, cadmium, zinc and copper from ceramic and glass wares available on the market in Poland and assessment of consumer exposure to these elements. Material and methods. Ceramic and glass articles which were available on the retail market and mainly produced in China were tested for release of lead, cadmium, zinc and copper. Samples for testing were prepared in accordance with European Standards: EN 1388-1 and EN 1388-2 and the migration of elements into a food simulant (4% acetic acid) was measured using flame atomic absorption spectrometry (FAAS). Validated and accredited methods according to EN ISO/ IEC 17025:2005 meeting the criteria set in the legislation were applied. Exposure assessment was performed taking into account actual reference doses introduced by the European Food Safety Authority (EFSA) and the Joint FAO/WHO Expert Committee on Food Additives (JECFA). Results. 736 samples of ceramic and glass wares were tested. Among investigated samples for migration of lead 82% of results were below limit of quantification (LOQ = 0.1 mg/L) of the analytical method used. For cadmium zinc and copper results below LOQ were found in 94%, 79% and 100% tested samples, respectively (Cd LOQ = 0.01mg/L; Zn LOQ = 0.05 mg/L; Cu LOQ = 0.03 mg/L). Only one sample release lead in amount higher than limit set in Polish Standard PN-B-13210:1997, it was rim of the glass mug and migration value was 4.81 mg/article. In case of cadmium there were two samples which exceeded permissible migration limit, it was flat ceramic dish and the rim of the glass mug, migration values were: 0.14 mg/dm2 and 0.42 mg/article respectively. The most measurable results (above LOQ) in case of lead and cadmium were for the samples of ceramic and glass drinking vessels. Quantifiable amounts of zinc were found also in other groups of articles tested: flat and deep ceramic dishes. None of the tested articles released copper in amount higher than LOQ value. The risk assessment showed that lead and cadmium exposure for some of the samples far exceed the reference doses. For children, assuming a single use only of these vessels, these doses may be exceeded: in the case of lead, 69 times and in the case of cadmium, 8 times. Conclusions. It is the urgent need to introduce requirements into the applicable legislation for the rim area of drinking ceramic and glass vessels to reduce exposure especially by the most vulnerable groups of population such as children.
W artykule przedstawiono zagadnienia związane z działalnością Komisji Kodeksu Żywnościowego ze szczególnym uwzględnieniem prac Komitetu Kodeksu Żywnościowego FAO/WHO ds. Zanieczyszczeń Żywności. Zwrócono uwagę na bieżące tematy poruszane przez ten Komitet istotne z punktu widzenia bezpieczeństwa żywności i handlu międzynarodowego, jak również niektóre ważne dokumenty opracowane w przeszłości w tym zakresie dotyczące metali ciężkich, takich jak ołów, kadm, rtęć czy arsen.
W artykule przedstawiono aktualny stan prawny w zakresie zanieczyszczenia żywności ołowiem i arsenem oraz planowane od stycznia 2016 r. zmiany w ustawodawstwie w tym zakresie i wprowadzenie nowych wymagań. Szczegółowo omówiono zmiany w ustawodawstwie UE oraz „Ogólnej normie kodeksowej dotyczącej zanieczyszczeń i toksyn w żywności i paszach” (GSCTFF) w świetle prac Europejskiego Urzędu ds. Bezpieczeństwa Żywności (EFSA), Komitetu Ekspertów Komisji Europejskiej ds. Środowiskowych i Przemysłowych Zanieczyszczeń Żywności, Połączonego Komitetu Ekspertów ds. Dodatków do Żywności oraz Komitetu Kodeksu Żywnościowego FAO/WHO ds. Zanieczyszczeń Żywności w odniesieniu do ołowiu i arsenu nieorganicznego.
W artukule przedstawiono informacje dotyczące potencjalnego ryzyka dla zdrowia związanego ze spożyciem wodorostów morskich z uwzględnieniem stwierdzanego poziomu zanieczyszczenia pierwiastkami szkodliwymi dla zdrowia. Oceny dokonano na podstawie wyników badań własnych oraz danych zgromadzone przez państwa członkowskie UE. Omówiono aktualny stan prawny w tym obszarze oraz działania podjęte przez Komisję Europejską zmierzające do właściwego zarządzania ryzykiem. Zwrócono również uwagę na powiadomienia zgłaszane w ramach systemu Wczesnego Ostrzegania o Niebezpiecznej Żywności i Paszach (RASFF), dotyczące stwierdzenia istotnego zagrożenia dla zdrowia związanego z wysoką zawartością metali ciężkich w wodorostach morskich i suplementach diety je zawierających.
W artykule przedstawiono aktualne prace Komisji Europejskiej dotyczące zanieczyszczenia żywności rtęcią oraz planowaną w związku z tym zmianę i ujednolicenie ustawodawstwa. Omówiono również ostatnie opinie Europejskiego Urzędu ds. Bezpieczeństwa Żywności na lemat korzyści i ryzyka związanego ze spożyciem ryb oraz prace ekspertów FAO/WHO, które przyczyniły się do podjęcia działań z tego zakresu. Przedstawiono również powiadomienia z okresu 2013-2015 w ramach systemu RASFF dotyczące rtęci w żywności.
Background. In addition to the release of lead and cadmium from ceramic and glass vessels, (acceptable limits being set by the EU 84/500/EC Directive), other harmful metals can migrate, such as nickel and chromium. Permissible migration limits for these latter metals however have not yet been set in the EU legislation. Both the toxic properties of nickel and chromium and the measures taken by the European Commission Working Group on Food Contact Materials for verifying permissible migration limits for lead, cadmium and other metals from ceramics have acted as drivers for studies on nickel and chromium release from ceramic and glass tableware. Objective. To investigate the migration of nickel and chromium into food simulants from ceramic and glassware, available on the Polish market, which are intended for coming into contact with food. Potential consumer exposure can thereby be estimated from the release of these elements into food. Materials and Methods. Tableware consisted of ceramics and glass vessels generally available on the domestic market, with inner surfaces being mainly coloured and with rim decorations. Migration of nickel and chromium studied from the ceramics was carried out in 4% acetic acid (24 ± 0.5 hrs at 22 ± 2°C), whilst that from glassware in 4% acetic acid (24 ± 0.5 hrs at 22 ± 2°C) and 0.5% citric acid (2 ± 0.1 hrs at 70 ± 2°C). The concentrations of metals which had migrated into the test solutions were measured by using flame atomic absorption spectrometry (FAAS). This analytical procedure had been previously validated by measuring nickel and chromium released into food simulants from ceramic and glass tableware where working ranges, detection limits, quantification limits, repeatability, accuracy, mean recovery and uncertainty were established. Results. Migration of nickel and chromium was measured from 172 ceramic and 52 and glass vessels samples, with all results being below the limits of quantification (LOQ = 0.02 mg/L), excepting one instance where a 0.04 mg/L concentration of nickel was found. The validated methods for measuring chromium achieved the following parameters; 0.02 to 0.80 mg/L operating range, 0.01 mg/L detection limit, 0.02 mg/L limit of quantification, 6% repeatability, 2.8% accuracy, 102% average recovery and 11% uncertainty. For the nickel method the corresponding parameters were 0.02 to 0.80 mg/L working range, 0.02 mg/L limit of quantification, 0.01 mg/L detection limit, 5% repeatability, 6.5% accuracy, 101% average recovery and 12% uncertainty. Conclusions. The tested ceramics and glassware did not pose a threat to human health regarding migration of nickel and chromium, and thus any potential exposure to these metals released from these products into food will be small. However, due to the toxicity of these metals, the migration of nickel and chromium is still required for articles coming into contact with food, which includes metalware.
W artykule omówiono zagrożenie dla zdrowia spowodowane zanieczyszczeniem żywności glinem w świetle opinii Europejskiego Urzędu ds. Bezpieczeństwa Żywności oraz Połączonego Komitetu Ekspertów FAO/WHO ds. Substancji Dodatkowych. Ponadto przedstawiono informacje na temat źródeł zanieczyszczenia żywności tym pierwiastkem, aspekty toksykologiczne i legislacyjne. W artykule przedstawiono również powiadomienia z okresu 2013-2018 w ramach systemu RASFF dotyczące zanieczyszczenia środków spożywczych aluminium oraz migracji tego pierwiastka z materiałów i wyrobów przeznaczonych do kontaktu z żywnością.
W artykule przedstawiono informacje dotyczące zagrożenia dla zdrowia związanego z obecnością niklu w żywności i wodzie przeznaczonej do spożycia przez ludzi w świetle ostatniej opinii Europejskiego Urzędu ds. Bezpieczeństwa Żywności (EFSA) z 2015 r. Ustawodawstwo Unii Europejskiej nie podaje limitów zawartości niklu w środkach spożywczych, jednak Komisja Europejska opracowała zalecenie dotyczące monitoringu niklu w żywności, które ma być realizowane wiatach 2016-2018.
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Natural medicinal resources are a country’s natural wealth. Natural medicinal waters, medicinal gases, and peloids have many properties that enable their use in the treatment of gastrointestinal, circulatory, respiratory, bone and joint, and skin and soft tissue disorders. Balneotherapy can be also applicable in prevention of many diseases and rehabilitation. At present, because there are several chemicals of synthetic origin, there is a need to search for nonpharmacological approaches and explore natural healing sources, which better fit the human body. Compared to synthetic drugs, these resources rarely show side effects, which increases the comfort of therapy. The use of natural medicinal resources in the form of treatments in health resort medicine centers under the supervision of balneologists, combined with the healing properties of the climate, contributes not only to the reduction of treatment time for many diseases but also to improvement of therapy’s results. The article discusses natural medicinal resources and some of their therapeutic applications.
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Background. Inorganic forms of arsenic are much more highly toxic to humans than organic species. Their effects include being carcinogenic, genotoxic and neurotoxic, where in the latter case, above all, they affect nervous system development in the foetus, infants and children. The main foodstuffs contributing significantly to its total dietary intake are drinking water, rice (and its products), fish, seafood, cereals, seaweed, root vegetables, food supplements, mushrooms and tea. After water, tea is the second most popular beverage drunk in Poland with average consumption annually indicating that statistically every Polish inhabitant drinks at least one cup of tea daily. Objectives. The aim of the study was to determine the total and inorganic content of arsenic in various black and green teas available on the market and thus to estimate consumer exposure to inorganic arsenic from this foodstuff. Materials and Methods. Analyses of total and inorganic arsenic were performed on 23 samples of black and green teas that consisted of tea leaves, teas in bags and granules, from various sources. The analytical method was hydride generation atomic absorption spectrometry (HGAAS), after dry ashing of samples and reduction of arsenic to arsenic hydride using sodium borohydride. In order to isolate only the inorganic forms of arsenic prior to mineralisation, samples were subjected to concentrated HCl hydrolysis, followed by reduction with hydrobromic acid and hydrazine sulphate after which triple chloroform extractions and triple 1M HCl re-extractions were performed. Exposure of adults was estimated in relation to the Benchmark Dose Lower Confidence Limit (BMDL05) as set by the Joint FAO/WHO Expert Committee on Food Additives (JECFA) that resulted in a 0.5% increase in lung cancer (3.0 μg/kg body weight (b.w.) per day). Results. Green teas were found to be more highly contaminated with both total and inorganic arsenic than black teas. Contamination of black teas total and inorganic arsenic was mean: 0.058 mg/kg (median: 0.042 mg/kg, 90th percentile: 0.114 mg/kg), and 0.030 mg/kg, (median: 0.025 mg/kg, 90th percentile: 0.030 mg/kg) respectively. Whilst for the green teas, these were correspondingly mean total arsenic content: 0.134 mg/kg (median: 0.114 mg/kg, 90th percentile: 0.234 mg/kg) and inorganic arsenic, mean: 0.100 mg/kg (median: 0.098 mg/kg, 90th percentile: 0.150 mg/kg). The estimated average adult exposures to inorganic arsenic in black and green tea were less than 1% of the BMDL05. Green tea samples, with the highest measured inorganic arsenic, were found to cause an intake exceeding 0.5% of the BMDL05 value. However when the drinking water is also accounted for when teas are prepared, then the exposure from black and green tea becomes exceeding 0.7% and 1.3% of the BMDL05 value respectively. Conclusions. Findings thus demonstrate that drinking black or green teas does not pose a significant health threat to consumers, even though contaminations in some individual samples were significant.
Background. Rice is a staple food for many people in the world and an important ingredient for production of food for infants and young children. According to European Food Safety Authority (EFSA), cereals, primarily rice and rice products, are an important source of human exposure to inorganic arsenic, which has been classified by the International Agency for Research on Cancer (IARC) as group I carcinogen. Arsenic is present in rice and rice products mainly as an inorganic form being more toxic than organic compounds. Objectives. The aim of the study was to determine the total and inorganic arsenic content in rice, rice-based products including food for infants and young children available on the market in Poland and thus to estimate consumer exposure to inorganic arsenic from these groups of foodstuffs. Materials and Methods. A total of 62 samples of rice and rice products from trade, including a group of rice products for infants and young children, were tested. Contents of total and inorganic arsenic were determined by using hydride generation atomic absorption spectrometry (HGAAS), after dry mineralization of samples and reduction of arsenic to arsenic hydride with sodium borohydride. To extract the inorganic arsenic forms, the samples were subjected to hydrolysis in concentrated HCl and then reduced in the presence of hydrobromic acid and hydrazine sulphate after which triple chloroform extractions and triple 1M HCl re-extractions were performed. Exposure of different groups of populations (adults and children), was estimated in relation to the Benchmark Dose Lower Confidence Limit (BMDL05) as set by the Joint FAO/WHO Expert Committee on Food Additives (JECFA) that resulted in a 0.5% increase in lung cancer (3.0 μg/kg body weight (b.w.) per day). Results. Mean content of total and inorganic arsenic in investigated rice samples was 0.12 mg/kg (median: 0.09 mg/kg; 90th percentile 0.22 mg/kg) and 0.04 mg/kg (median: 0.03 mg/kg, 90th percentile 0.07 mg/kg). Brown rice was found to be more highly contaminated with both total and inorganic arsenic than white rice. Mean contamination of brown rice with total arsenic and inorganic arsenic was: 0.18 mg/kg (median: 0.12 mg/kg, 90th percentile: 0.32 mg/kg) and 0.05 mg/kg (median: 0.05 mg/kg, 90th percentile: 0.07 mg/kg). In turn for the white rice contamination was lower, mean total arsenic content: 0.10 mg/kg (median: 0.08 mg/kg, 90th percentile: 0.19 mg/kg) and mean inorganic arsenic: 0.03 mg/kg (median: 0.03 mg/kg, 90th percentile: 0.06 mg/ kg). Contamination of rice-based products both total and inorganic arsenic was similar to those reported for rice, except rice wafers (mean: 0.24 mg/kg and 0.13 mg/kg). In the group of products for infants and young children obtained results were low – mean total arsenic content was 0.06 mg/kg and inorganic arsenic 0.02 mg/kg. The estimated average adult and children’s exposure to inorganic arsenic with rice and rice products was less than 1% of the BMDL05. Intake of inorganic arsenic by 12-month-old infants with ricebased products intended for this group of population was at 6% BMDL05. Conclusions. Based on the obtained results, it was found that the content of total and inorganic arsenic in investigated samples of rice and rice products did not pose a health risk even though contamination levels in some individual samples were significant.
Omówiono i uzasadniono zmiany, które miały ostatnio miejsce w ustawodawstwie UE w zakresie najwyższych dopuszczalnych poziomów kadmu w środkach spożywczych. Szczególne znaczenie ma uzgodnienie wymagań dotyczących dopuszczalnego zanieczyszczenia produktów przeznaczonych dla niemowląt i małych dzieci. Wymagania dla tej grupy produktów, podane w rozporządzeniu Komisji (UE) nr 488/2014 z 12 maja 2014 r. zmieniającym rozporządzenie Komisji (WE) nr 1881/2006 w odniesieniu do najwyższych dopuszczalnych poziomów kadmu w środkach spożywczych, będą obowiązywać od 1 stycznia 2015 r. Oceniono także zagrożenie dla zdrowia spowodowane zanieczyszczeniem żywności tym pierwiastkiem w krajach Unii Europejskiej w świetle ostatniego opracowania Europejskiego Urzędu ds. Bezpieczeństwa Żywności (EFSA) z 2012 r. "Cadmium dietary exposure in the European population", a także przedstawiono zalecenia Komisji mające na celu ograniczenie obecności kadmu w środkach spożywaych.
Background. The dietary intake of harmful elements, particularly lead and cadmium constitutes a health threat and essential measures should be undertaken to reduce consumer exposure. The latest risk assessments by the European Food Safety Authority (EFSA) and Joint FAO/WHO Expert Committee on Food Additives (JECFA) have indicated that the Provisional Tolerable Weekly Intake (PTWI) for lead and cadmium do not ensure health safety and their review had to be undertaken. Migration from ceramics and glassware intended for food contact is an important source of lead and cadmium intake. Objectives. To study the release of lead and cadmium from ceramics and glassware (including decorated products) intended for food contact that are available on the Polish market and to assess the resulting health risk to the consumer. Materials and Methods. Ceramics and glassware (mainly decorated) were sampled from the Polish market during 2010- 2012 throughout the country by staff of the Sanitary-Epidemiological Stations in accordance with monitoring procedures and guidelines designed by the National Institute of Public Health-National Institute of Hygiene. Migration of lead and cadmium was measured by incubating the samples with 4% acetic acid for 24 hours at a temperature of 22±2ºC in the dark. Flame Atomic Absorption Spectrometry (FAAS) was used to measure these elements in food simulant according to a validated and accredited method (PN-EN ISO/IEC 17025). Results. 1273 samples of ceramics and glass wares were analysed in 2010-2012. Lead and cadmium release were usually found to be below analytical detection limits. Permissible migration limits (as prescribed by the legislation) of these metals were rarely exceeded and were reported mainly in articles imported from outside the EU. Two imported and decorated ceramic flat plates released lead at 0.9 and 11.9 mg/dm2 (limit 0.8 mg/dm2) and 5 imported deep plates gave migration values of 4.7 mg/L, 4.9 mg/L, 5.6 mg/L, 6.1 mg/L, 8.6 mg/L (limit 4.0 mg/L). Lead migrations from ceramic ware rims above the 2.0 mg per product limit (as established in Polish Standard PN-B-13210:1997 [16]) were observed in 4 samples, at 2.1, 3.7, 4.2 and 14.4 mg per product, respectively. Migrations of cadmium from the ceramic samples’ rims were within permissible limits. Majority of high migration results were obtained for decorated rims of glass vessels for beverages. The highest migration from the rim of an imported glass mug was reported at 163.8 mg/product for lead and at 8.96 mg/product for cadmium. Risk assessment indicated that exposures to lead and cadmium released from ceramic wares based on the migration limits set by the EU legislation lead to human intake close to, or exceeding reference doses. For a 20 kg b.w. child the lead BMDL01 value could thus be exceeded by over 30-fold and the cadmium TWI value 4-fold. Conclusions. Review of EU legislation applicable to lead and cadmium migration limits from ceramics is necessary with an intention to lower such limits. The limits applied to the rims of ceramics and glassware intended for beverages should be included. The release of lead and cadmium at the maximum permissible levels for ceramics may lead to uptakes becoming hazardous to human health. Appropriate measures are thus necessary to reduce sources of exposure.
W artykule podano informacje dotyczące toksyczności, metabolizmu oraz przemian rtęci w środowisku, a także źródeł narażenia na rtęć i jej organicznych połączeń. Omówiono dane pochodzące z monitoringu w Polsce i w innych krajach, obrazujące zanieczyszczenie środków spożywczych rtęcią. Oszacowano zagrożenie dla zdrowia spowodowane zanieczyszczeniem żywności rtęcią w świetle ostatnich opinii: Europejskiego Urzędu ds. Bezpieczeństwa Żywności (EFSA) z 2012 r. oraz Połączonego Komitetu Ekspertów FAO/WHO ds. Substancji Dodatkowych (JECFA) z 2010 r. Przedstawiono zalecenia dla konsumentów opracowane przez Komisję Europejską i państwa członkowskie w odniesieniu do spożycia ryb drapieżnych, uwzględniające najbardziej wrażliwe grupy populacji - kobiety planujące dążę, ciężarne, karmiące matki oraz dzieci. W artykule przedstawiono również powiadomienia z lat 2010-2012 w ramach systemu RASFF dotyczące rtęci w żywności.
Background. According to the European Food Safety Authority (EFSA), fish, seafood and seaweeds are foodstuffs that significantly contribute to dietary arsenic intake. With the exception of some algal species, the dominant compounds of arsenic in such food products are the less toxic organic forms. Both the Joint FAO/ WHO Expert Committee on Food Additives (JECFA) and EFSA recommend that speciation studies be performed to determine the different chemical forms in which arsenic is present in food due to the differences in their toxicity. Knowing such compositions can thus enable a complete exposure assessment to be made. Objectives. Determination of total and inorganic arsenic contents in fish, their products, seafood and seaweeds present on the Polish market. This was then followed by an exposure assessment of consumers to inorganic arsenic in these foodstuffs. Materials and Methods. Total and inorganic arsenic was determined in 55 samples of fish, their products, seafood as well as seaweeds available on the market. The analytical method was hydride generation atomic absorption spectrometry (HGAAS), after dry ashing of samples and reduction of arsenic to arsenic hydride using sodium borohydride. In order to isolate only the inorganic forms of arsenic prior to mineralisation, samples were subjected to concentrated HCl hydrolysis, followed by reduction with hydrobromic acid and hydrazine sulphate after which triple chloroform extractions and triple 1M HCl re-extractions were performed. Exposure of adults was estimated in relation to the Benchmark Dose Lower Confidence Limit (BMDL05) as set by the Joint FAO/WHO Expert Committee on Food Additives (JECFA) that resulted in a 0.5% increase in lung cancer (3.0 μg/kg body weight (b.w.) per day). Results. Mean total arsenic content from all investigated fish samples was 0.46 mg/kg (90th percentile 0.94 mg/kg), whilst the inorganic arsenic content never exceeded the detection limit of the analytical method used (0.025 mg/kg). In fish products, mean total arsenic concentration was 1.48 mg/kg (90th percentile: 2.42 mg/kg), whilst in seafood they were 0.87 mg/ kg (90th percentile: 2.23 mg/kg), for inorganic arsenic contamination at the 90th percentile was 0.043 mg/kg with most results however being less than 0.025 mg/kg. The highest inorganic arsenic levels were determined in the Hijiki algal species samples (102.7 mg/kg), whereas the other algal samples gave a mean inorganic concentration of 0.41 mg/kg (90th percentile 0.86 mg/kg). The estimated average adults exposure to inorganic arsenic in fish, seafood and seaweeds was less than 0.5% of the lowest BMDL0.5 dose. Only for the Hijiki seaweed it was at 4.9% BMDL0.5. Conclusions. Results demonstrate that dietary arsenic intake from fish, seafood and seaweed along with all their products do not constitute a significant health threat to consumers apart from the seaweed species Hizikia fusiformis in which over 40% of all the inorganic arsenic compounds were found.
W artykule omówiono podstawowe zasady dotyczące działania systemu Wczesnego Ostrzegania o Niebezpiecznych Produktach Żywnościowych i Środkach Żywienia Zwierząt - RASFF. Przedstawiono rodzaje zagrożeń oraz powiadomień dotyczących materiałów i wyrobów przeznaczonych do kontaktu z żywnością, jakie w ostatnich latach były przedmiotem notyfikacji do systemu RASFF.
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