efsa-opinion-chromium-food-drinking-water

efsa-opinion-chromium-food-drinking-water efsa-opinion-chromium-food-drinking-water

damienvanherp
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16.04.2014 Views

Chromium in food and drinking water Eastern Sterea Hellas (central Euboea and Asopos valley), central Greece, at concentrations sometimes exceeding the Greek and EU drinking water regulatory limit for total chromium of 50 µg/L. Water contamination by Cr(VI) species in central Euboea was mainly linked to natural processes, although there were cases when it seemed of anthropogenic origin. In Asopos valley Cr(VI) presence was associated to industrial wastes. While the presence of Cr(VI) and/or its precursors in drinking water is often evidence/consequence of anthropogenic activity, over the last years there have been several reports of naturally occurring Cr(VI) in groundwater (McNeill et al., 2012a). Although in most cases the Cr(VI) concentrations found appear to be in the order of a few µg/L or some tens of µg/L, values of a few hundreds of µg/L are not unusual. Food preparation Food preparation may increase food chromium content, the increase depending on the process (Stoewsand et al., 1979; Offenbacher and Pi-Sunyer, 1983; Kumpulainen, 1992): for instance, stainless steel utensils used in food preparation may contribute to chromium levels. Likewise, chromium may be present in acidic fruit juices as a result of the contact with stainless steel equipment or utensils. There are various factors that may affect the release of chromium into acidic foods coming in contact with stainless steel surfaces, such as: contact area, pH of the food product, food temperature during contact and duration of contact, agitation, presence of organic chelating constituents in the food (e.g. citric acid), and particular features of the metal alloy. However, large percentages of chromium can also be removed from foods during food processing other than preparation (Schroeder, 1971, 1974; Anderson, 1981). It can be observed that the forms of chromium leaching into foods during food preparation should contain mainly or exclusively the trivalent metal due to both the reducing characteristics of the environment and the fact that Cr(III) is its most stable oxidation state. The increased concentrations of chromium in foods possibly consequent to leaching, have the potential to contribute measurably to chromium dietary exposure (Stoewsand et al., 1979; Offenbacher and Pi- Sunyer, 1983). 1.2.3. Conclusions Chromium occurs in environmental compartments with highly variable levels. Unlike the large availability of total chromium data, Cr(VI) speciation appears to have been carried out on a relatively limited basis. The metal presence is determined by natural as well as anthropogenic factors, the latter identifiable primarily with industrial sources. Cr(III) and Cr(VI) can both be released into the air, the latter in general to a likely quite lesser extent. In air, chromium is present in the form of aerosols that are removed by wet and dry deposition. Chromium particles of small aerodynamic diameter (< 10 µm) may remain airborne for long periods and undergo long-range transport. Under normal conditions, airborne Cr(0) and Cr(III) forms do not undergo any reaction, whereas Cr(VI) eventually reacts with dust particles or other pollutants to yield Cr(III). In non-industrialized areas total chromium concentrations above 10 ng/m 3 are uncommon whereas in urban and industrialized areas they can be quite higher (from tens to hundreds of ng/m 3 ). As a result of smoking, chromium concentrations in indoor air have been reported as high as 1000 ng/m 3 . In rainwater, chromium concentrations on average fall in the range 0.2-1 µg/L, some part of which may be accounted for by Cr(VI). Surface runoff, deposition from air, and release of municipal and industrial waste waters are sources of chromium in surface waters. Cr(III) is lost from the aquatic environment primarily due to precipitation of hydrated Cr 2 O 3 followed by sedimentation. In surface waters, high concentrations of Cr(VI) forms can be found locally. The Cr(VI) anion species can persist in aquatic media, possibly for long periods, as water-soluble complexes: however, they will react with organic matter or other reducing agents to form Cr(III). Therefore, in surface waters rich in organic content, Cr(VI) is expected to have a shorter lifetime. Although in surface waters total chromium may be present at levels greater than 50 µg/L, in general the element is detected at concentrations in the order of few tens of µg/L or lower, rivers being more contaminated than lakes and sea water. EFSA Journal 2014;12(3):3595 20

Chromium in food and drinking water Total chromium concentrations in groundwater and water from drinking water sources/supplies may range from quite less than 1 µg/L up to a few µg/L, although cases of a high chromium occurrence have also been reported. Cr(VI) appears to be occasionally present in the aforesaid types of water, at levels in the range from a few up to some tens of µg/L and possibly higher. The presence of Cr(VI) in drinking water and/or its precursors is often evidence/consequence of anthropogenic contamination. As water treatment facilities use strong oxidants to potabilise water, in drinking water chromium may easily be present in the hexavalent state. 1.3. Previous risk assessments Chromium III IARC evaluated chromium and chromium compounds in 1990 and concluded that metallic chromium and Cr(III) compounds are not classifiable as to their carcinogenicity to humans (Group 3) (IARC, 1990). The U.S. Environmental Protection Agency (U.S. EPA, 1998a) established a reference dose (RfD) for metallic Cr(III) of insoluble salts of 1.5 mg/kg body weight (b.w.) per day based on a subacute and long-term feeding experiment in rats fed with chromic oxide pigment (Ivankovic and Preussmann, 1975). It was noted that the overall confidence in this RfD was low due to low confidence in the database and the lack of an observed effect level. As to its human carcinogenicity, trivalent chromium was classified as group D (not classified). In 2003 the Scientific Committee on Food (SCF) issued an opinion on the ‘Tolerable Upper Intake Level of Trivalent Chromium’ and concluded that the limited oral toxicity data available in animals as well as in humans did not give enough information on a dose-response relationship, and therefore a tolerable upper intake level that is likely to pose no risk of adverse health effects could not be derived (SCF, 2003). The UK Expert group on Vitamins and Minerals (EVM, 2003) concluded that there were insufficient data from human and animal studies to derive a safe upper level for Cr(III) although its oral toxicity appeared to be low (due also to low absorption). Based on a study of oral toxicity in rats administered with chromium chloride (Anderson et al., 1997), the EVM proposed that a total daily intake of about 0.15 mg/kg b.w. per day (or 10 mg/person) of Cr(III) would be expected to be without adverse health effects. The UK Committee on Mutagenicity of Chemicals in Food (COM), at the request of the UK Food Standards Agency (FSA), reviewed all the available data pertaining to the mutagenicity of Cr(III), particularly Cr(III) picolinate. The evaluation of the COM (COM, 2004) led to the overall conclusion that, taken all together, the data from the in vitro genotoxicity assays suggested that Cr(III) picolinate was negative with respect to genotoxicity. The Concise International Chemical Assessment Document (CICAD) (WHO/IPCS, 2009a) on inorganic trivalent chromium compounds, concluded that the key toxic endpoints for soluble inorganic Cr(III) salts were chronic respiratory toxicity on inhalation and contact sensitization of the skin, while oral toxicity was low. It was noted that there was no clear evidence of genotoxic and/or carcinogenic effects of trivalent chromium compounds, there were no effects on fertility and the widespread use of mainly organic Cr(III) complexes as food supplements at 10-fold or even higher dose levels than the suggested dietary intakes had not shown any consistent toxic effect. The EFSA evaluated the safety and efficacy of chromium methionine as a feed additive for all species in 2009 (EFSA, 2009a). The EFSA Panel on Additives and Products or Substances used in Animal Feed (FEEDAP Panel) noted that on the basis of the available literature Cr(III) may be a genotoxic compound under in vivo conditions and then considered it prudent to avoid any additional exposure of the consumers resulting from the use of supplementary Cr in animal nutrition. The EFSA evaluated the safety of chromium picolinate as a source of chromium added for nutritional purposes in food supplements in 2009 (EFSA, 2009b). The EFSA Panel on Food Additives and Nutrient Sources added to Food (ANS Panel) concluded that the use of picolinate as a source of Cr(III) EFSA Journal 2014;12(3):3595 21

Chromium in <strong>food</strong> and <strong>drinking</strong> <strong>water</strong><br />

Total <strong>chromium</strong> concentrations in ground<strong>water</strong> and <strong>water</strong> from <strong>drinking</strong> <strong>water</strong> sources/supplies may<br />

range from quite less than 1 µg/L up to a few µg/L, although cases of a high <strong>chromium</strong> occurrence<br />

have also been reported. Cr(VI) appears to be occasionally present in the aforesaid types of <strong>water</strong>, at<br />

levels in the range from a few up to some tens of µg/L and possibly higher. The presence of Cr(VI) in<br />

<strong>drinking</strong> <strong>water</strong> and/or its precursors is often evidence/consequence of anthropogenic contamination.<br />

As <strong>water</strong> treatment facilities use strong oxidants to potabilise <strong>water</strong>, in <strong>drinking</strong> <strong>water</strong> <strong>chromium</strong> may<br />

easily be present in the hexavalent state.<br />

1.3. Previous risk assessments<br />

Chromium III<br />

IARC evaluated <strong>chromium</strong> and <strong>chromium</strong> compounds in 1990 and concluded that metallic <strong>chromium</strong><br />

and Cr(III) compounds are not classifiable as to their carcinogenicity to humans (Group 3) (IARC,<br />

1990).<br />

The U.S. Environmental Protection Agency (U.S. EPA, 1998a) established a reference dose (RfD) for<br />

metallic Cr(III) of insoluble salts of 1.5 mg/kg body weight (b.w.) per day based on a subacute and<br />

long-term feeding experiment in rats fed with chromic oxide pigment (Ivankovic and Preussmann,<br />

1975). It was noted that the overall confidence in this RfD was low due to low confidence in the<br />

database and the lack of an observed effect level. As to its human carcinogenicity, trivalent <strong>chromium</strong><br />

was classified as group D (not classified).<br />

In 2003 the Scientific Committee on Food (SCF) issued an <strong>opinion</strong> on the ‘Tolerable Upper Intake<br />

Level of Trivalent Chromium’ and concluded that the limited oral toxicity data available in animals as<br />

well as in humans did not give enough information on a dose-response relationship, and therefore a<br />

tolerable upper intake level that is likely to pose no risk of adverse health effects could not be derived<br />

(SCF, 2003).<br />

The UK Expert group on Vitamins and Minerals (EVM, 2003) concluded that there were insufficient<br />

data from human and animal studies to derive a safe upper level for Cr(III) although its oral toxicity<br />

appeared to be low (due also to low absorption). Based on a study of oral toxicity in rats administered<br />

with <strong>chromium</strong> chloride (Anderson et al., 1997), the EVM proposed that a total daily intake of about<br />

0.15 mg/kg b.w. per day (or 10 mg/person) of Cr(III) would be expected to be without adverse health<br />

effects.<br />

The UK Committee on Mutagenicity of Chemicals in Food (COM), at the request of the UK Food<br />

Standards Agency (FSA), reviewed all the available data pertaining to the mutagenicity of Cr(III),<br />

particularly Cr(III) picolinate. The evaluation of the COM (COM, 2004) led to the overall conclusion<br />

that, taken all together, the data from the in vitro genotoxicity assays suggested that Cr(III) picolinate<br />

was negative with respect to genotoxicity.<br />

The Concise International Chemical Assessment Document (CICAD) (WHO/IPCS, 2009a) on<br />

inorganic trivalent <strong>chromium</strong> compounds, concluded that the key toxic endpoints for soluble inorganic<br />

Cr(III) salts were chronic respiratory toxicity on inhalation and contact sensitization of the skin, while<br />

oral toxicity was low. It was noted that there was no clear evidence of genotoxic and/or carcinogenic<br />

effects of trivalent <strong>chromium</strong> compounds, there were no effects on fertility and the widespread use of<br />

mainly organic Cr(III) complexes as <strong>food</strong> supplements at 10-fold or even higher dose levels than the<br />

suggested dietary intakes had not shown any consistent toxic effect.<br />

The EFSA evaluated the safety and efficacy of <strong>chromium</strong> methionine as a feed additive for all species<br />

in 2009 (EFSA, 2009a). The EFSA Panel on Additives and Products or Substances used in Animal<br />

Feed (FEEDAP Panel) noted that on the basis of the available literature Cr(III) may be a genotoxic<br />

compound under in vivo conditions and then considered it prudent to avoid any additional exposure of<br />

the consumers resulting from the use of supplementary Cr in animal nutrition.<br />

The EFSA evaluated the safety of <strong>chromium</strong> picolinate as a source of <strong>chromium</strong> added for nutritional<br />

purposes in <strong>food</strong> supplements in 2009 (EFSA, 2009b). The EFSA Panel on Food Additives and<br />

Nutrient Sources added to Food (ANS Panel) concluded that the use of picolinate as a source of Cr(III)<br />

EFSA Journal 2014;12(3):3595 21

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