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The information in the archive was published by MAFF, Department of Health and the Scottish Executive before April 1st 2000 when the Food Standards Agency was established.

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Food Surveillance Information Sheet


Number 122      August 1997

MAFF UK - SURVEY OF LEAD AND TIN IN CANNED FRUITS AND VEGETABLES


Index to MAFF UK Food Surveillance Information Sheets, 1997

See also:
146: MAFF UK - Concentrations of Metals and Other Elements in Selected Snack and Convenience Foods (March 1998)
149: MAFF UK - 1994 Total Diet Study (Part 2) Dietary Intakes of Metals and Other Elements (May 1998)
150: MAFF UK - Metals and Other Elements in Cows' Milk and Vegetables Produced Near Industrial Sites (May 1998)
151: MAFF UK - Concentrations of Metals and Other Elements in Marine Fish and Shellfish (May 1998)
152: MAFF UK - Summaries of Food Surveillance Papers - 'Lead, Arsenic and Other Metals in Food' and 'Cadmium, Mercury and Other Metals in Food' (June 1998)
155: MAFF UK - Lead in Dried Fruit (August 1998)
166: MAFF UK - Metals and Other Elements in Vegetarian Foods (November 1998)
179: MAFF UK - Tin in Canned Tomato Products (June 1999)
182: MAFF UK - Tin in Canned Pineapples (July 1999)
193: MAFF UK - Duplicate Diet Study of Vegetarians - Dietary Exposures to 12 Metals and Other Elements (January 2000)

Summary

A survey of lead and tin in canned fruits and vegetables was carried out between August 1996 and February 1997 on behalf of the Ministry of Agriculture, Fisheries and Food (MAFF) by Campden and Chorleywood Food Research Association. The aim of this survey was to determine the concentrations of lead and tin in a range of retail canned fruit and vegetable foods on sale in retail outlets in the UK. Concentrations of lead (mean 0.04 mg/kg, range <0.01 - 0.13 mg/kg) were similar to those previously reported for these foods and below the statutory limit for lead in all samples. Tin concentrations (mean 58 mg/kg, range 0.02 - 242 mg/kg) were broadly similar to previous results and, in all but two samples of gooseberries, below the statutory limit for tin. Relatively high levels of tin, still below the statutory limit, were found in some samples of other foods including asparagus, tomatoes, apricots and grapefruit. MAFF is planning a further study of individual cans of the products found to have higher tin contents in this study, to investigate the factors that influence their tin contents. Composite samples were analysed and it is not therefore possible to give results for individual branded samples.

Background

Lead

High levels of lead have, in the past, been found in canned foods, as a result of the use of lead-containing solder to seal can seams. However, since the 1980s this practice has been progressively phased out in the UK and in much imported produce, in favour of sealing by welding or, for certain foods, tin solder. This action was accompanied by a marked decline in lead content of canned foods,1 and canned foods now make only a minor contribution to overall dietary lead intakes. Intakes of lead from consumption of canned vegetables, estimated from the Total Diet Study (TDS), fell from 0.007 mg/day in 1982 to less than 0.001 mg/day in 1991. The intake of lead from fruit products fell from 0.005 mg/day to 0.001 mg/day over the same period. Samples from the present survey were analysed for lead to provide current data to monitor this trend.

The Lead in Food Regulations 1979,2 as amended, set a general limit for lead in foods of 1 mg/kg, with specific limits for certain foods which are listed in the Schedule to the Regulations. The Joint Food and Agriculture Organisation/World Health Organisation Joint Expert Committee on Food Additives and Contaminants (JECFA) has set a Provisional Tolerable Weekly Intake (PTWI) for lead of 0.025 mg/kg body weight.3 This corresponds to approximately 0.21 mg/day for a 60 kg adult. The dietary intake of lead estimated from the 1991 TDS was 0.028 mg/day, well below the PTWI.4

Tin

Tin is present naturally in foods although the tin content is generally below 1 mg/kg. The major dietary source of tin is canned foods, which often contain higher concentrations of tin than the unprocessed food, usually as a result of the dissolution of the tin coating of the can. The Tin in Food Regulations 1992 set a maximum permissible tin content of 200 mg/kg in foods for sale in or import to the UK.5 Previous MAFF surveys of tin in canned foods have shown that the majority of canned foods on sale in the UK comply with this limit, but with typically a few percent of samples containing in excess of 200 mg/kg tin.1

JECFA has set a PTWI for inorganic tin of 14 mg/kg body weight, which applies to chronic exposure. This is equivalent to 120 mg/day for a 60 kg adult.6 Tin in canned foods is likely to be present predominantly if not entirely in the inorganic form.

The most recent estimate of the dietary intake of tin from the typical UK diet was reported in 1994, for analysis of samples from the 1991 UK Total Diet Study.4 The estimated average intake was 5.3 mg/day. Although still well below the PTWI, this value was significantly higher than estimates for previous years (e.g. 2.0 mg/day in 1987 and 2.2 mg/day in 1985). The increase was mainly attributable to an increase in the tin content of canned vegetables samples (93 mg/kg in 1991 compared with 26 mg/kg in 1987, and 24 mg/kg in 1985). Canned vegetables contributed 66 per cent of the total tin intake in 1991, with fruit products (including canned fruits) contributing a further 25 per cent. In view of these results, the Food Advisory Committee recommended that further work be undertaken to identify the foods and mechanisms responsible for the apparent increase in the tin content of canned vegetables.

Campden and Chorleywood Food Research Association were commissioned to undertake this survey. Samples of a wide range of canned fruit and vegetable products were purchased from retailers for analysis and these are listed in Table 2. Foods were purchased from retail outlets in the North, Midlands and South of England to identify any regional variations in the concentrations of lead and tin present.

Method

Composite samples of each of 33 food types were analysed from three regions (North, Midlands and South of England). One composite sample of pasta sauce was also analysed. This brought the total number of samples to 100. The food types analysed are listed in Table 2. Each composite sample consisted of up to eight different brands of the same type of food.

To prepare each composite sample, the individual brands making up a food type were blended separately then added together in equal weights and blended further. Before blending each food was prepared following normal domestic practices (e.g. brine was drained from canned vegetables, etc.), but were not cooked. Analyses for lead and tin were carried out using procedures accredited by the United Kingdom Accreditation Service (UKAS), based on atomic absorption spectrophotometry by a flame method or, for samples containing low levels of tin, by hydride generation. Limits of determination of 0.01 mg/kg for lead and 0.05 mg/kg for tin were achieved. All samples were analysed in duplicate and the results reported as the means of duplicate analyses. Mean results were accepted only if the individual results remained within the following tolerances from the mean value: for lead, ±0.03 mg/kg; for tin, ±0.05 mg/kg (values below 5 mg/kg), ±5 mg/kg (values below 100 mg/kg) or ±5 per cent (values over 100 mg/kg).

Results

The lead and tin concentrations in composite samples are summarised in Table 2. Results are given for composite samples from each region and as a mean over the three regions. There was no significant regional variation in concentrations of lead and tin in foods purchased from the North, Midlands and South of England.

Interpretation

Lead

The lead concentrations in all samples were below the appropriate statutory limits. The mean lead content of canned vegetables was 0.02 mg/kg (range <0.01-0.05 mg/kg) and that of canned fruits 0.05 mg/kg (range <0.01-0.13 mg/kg). These values are similar to previous data, for example those from the 1991 TDS for canned vegetables (mean 0.02 mg/kg, range 0.01-0.04 mg/kg) and fruit products (which includes canned fruits; mean 0.03 mg/kg, range 0.01-0.06 mg/kg).

Tin

The tin contents of two composite samples of gooseberries were over 200 mg/kg, so one or both of the two individual cans that made up each of these samples will have exceeded the statutory limit. Some composite samples of other foods, for example tomatoes, asparagus, apricots and grapefruit, contained relatively high levels of tin (i.e. mean across all three regions >100 mg/kg), though still below the limit. It is possible that one or some of the individual cans making up these composite samples could have exceeded the statutory limit. All these foods are known to be relatively aggressive to tin and high values have been reported in previous work.1 The overall spread of results and the proportion of samples that exceed the statutory limit in this survey is also similar to those found in 1983-87.1

The mean tin concentration in canned vegetables was 44 mg/kg (range 0.02-165 mg/kg). This is somewhat lower than the value of 93 mg/kg (range 23-218 mg/kg) found for canned vegetables in the 1991 TDS (and which prompted this study), and is closer to values from earlier TDS. The mean tin content for canned fruits in the present study was 67 mg/kg (range 7.6-242 mg/kg), higher than that found for fruit products in the 1991 TDS (mean 32 mg/kg, range 7.6-86 mg/kg).

As the number and type of different foods sampled and their preparation in this study were different from those from the TDS, it is not possible to state with certainty whether the present results for tin reflect a trend since 1991. A project to analyse samples from the 1994 TDS for tin (and other elements) will be completed and reported this year and should help to clarify whether the results from the 1991 TDS were anomalous. The present study does however provide current data on the levels of tin in a wide range of canned fruits and vegetables. MAFF is considering a further study of individual cans of the products found to have higher tin contents in this study, to elucidate further the factors that influence their tin contents.

No significant differences were seen between the lead and tin contents of fruits packed in juice compared with the same fruits packed in syrup.

Intakes of lead and tin

Dietary intakes of lead and tin by mean and high-level adult consumers have been estimated, assuming that all canned fruits and canned vegetables contain lead and tin at the highest levels reported for these foods in the current study, and that all other foods contain lead and tin at the mean levels found in the 1991 TDS. These estimates are shown in Table 1. This scenario is very unlikely, especially for long-term consumption, and therefore represents an extreme worst-case estimate of intakes. Nevertheless, total dietary intakes of tin estimated even on this basis, while higher than corresponding estimates based on the 1991 TDS alone, remain well below the PTWI. Intakes of lead do not differ significantly from those estimated from the 1991 TDS alone, and again are well within the PTWI. Therefore the levels of lead and tin found in this study do not represent a long-term risk to consumers.

Acute effects due to tin have been reported following consumption of canned foods, especially acid fruit juices, with tin contents above 250 mg/kg. These effects are due to gastric irritation. Any such products on sale in the UK would of be in breach of The Tin in Food Regulations 1992. All samples in the present study contained less than 250 mg/kg tin, although as these are composite samples it is not possible to state whether this value was exceeded in individual cans making up the composite samples with the highest tin contents.

The results of this survey have been circulated to the Local Authorities Co-ordinating Body on Trading Standards (LACOTS) for information. MAFF will also be circulating this Information Sheet to trade, retail and consumer groups on publication, and inviting their comments.

References
  1. Meah, M.N., Smart, G.A., Harrison, A.J., Sherlock, J.C. (1991). Lead and tin in canned foods: Results of the UK survey 1983-1987. Food Additives and Contaminants, 8, 485.
  2. The Lead in Food Regulations 1979 (S.I. [1979] No. 1254), as amended by The Lead in Food (Amendment) Regulations 1985 (S.I. [1985] No. 912). HMSO.
  3. World Health Organisation (1993). Evaluation of Certain Food Additives and Contaminants. Forty-First Report of the Joint FAO/WHO Expert Committee on Food Additives. WHO Technical Report Series No.837. WHO, Geneva.
  4. MAFF Food Safety Directorate (1994). Food Surveillance Information Sheet Number 34: 1991 Total Diet Study.
  5. The Tin in Food Regulations 1992 (S.I. [1992] No. 496). HMSO.
  6. World Health Organisation (1989). Evaluation of Certain Food Additives and Contaminants. Thirty-Third Report of the Joint FAO/WHO Expert Committee on Food Additives. WHO Technical Report Series No. 776. WHO, Geneva
Contact Point

Further information can be obtained from:

Dr Patrick Miller
MAFF, Joint Food Safety and Standards Group
Food Contaminants Division
Room 238
Ergon House, c/o Nobel House
17 Smith Square
London, SW1P 3JR.

Tel: +44 (0)20 7238 5751
Fax: +44 (0)20 7238 5331


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These pages were last updated on July 31st 1997

 
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