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The duplicate method is very burdensome for the consumer and does not allow any investigation of which individual foods contribute most to dietary intake The second approach is an indirect method Exposure estimates are calculated by combining the concentrations of contaminants in individual foods (occurrence data) with the amounts of those foods that are eaten (consumption data) Occurrence data may be collected from a range of monitoring.

(1415)

programs Consumption data may be collected through food composition surveys at an individual consumer or household level Alternatively, consumption data may be estimated through food purchase statistics There are obvious disadvantages to each method of consumption estimation: food purchase statistics will only provide data on the quantities of food that are purchased, they do not allow for food wastage Food consumption surveys involve food frequency questionnaires consumers may be asked to keep a record of their consumption or be interviewed and asked to recall their consumption Dietary recall interviews can be awed because consumers do not remember precisely what was eaten; similarly, consumers may not always wish to state exactly how much of a so-called bad food was consumed! Because our diets are extremely complicated and highly variable, it is possible that some foods may not be consumed during the monitoring period.

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When comparing exposure estimates made using the indirect method, regard must be paid to the method of collection of consumption data: data collected over a longer monitoring period are more likely to reduce some of the possible error from variation in dietary habits Table 212 summarizes the results of the Swiss Federal Of ce of Public Health investigation into dietary exposure to acrylamide A duplicate diet study was used to investigate the acrylamide intake of 27 Swiss adults over a two-day period Duplicate samples of foods were collected and homogenized to yield composite samples of different meals (breakfast, lunch, dinner, snacks, and coffee) A mean daily intake of 0277 g kgbw 1 day 1 was estimated (67) It is interesting to note that coffee was shown to contribute the most acrylamide to the total intake.

This distance measure is called the Chi-square distance because of its similarity to the statistic used in the Chi-square test When the p variables are independent of each other and p is large (eg, greater than 30), the Chi-square statistic in Formula 1415 follows approximately a normal distribution according to the central limit theorem, no matter what distribution each of the p variables has With the mean and standard deviation of the Chi-square distance estimated 2 from a sample of the Chi-square distance values as X 2 and S X , the control limits for monitoring 2 X can be set to the following:

On reviewing the results of the duplicate diet study, the Swiss Federal Of ce of Public Health found that consumption of deep fried, baked, and roast potatoes, and crisps reported was below average Owing to the relatively high concentrations of acrylamide commonly found in these foods, it was decided to correct the possible underestimation By taking into account import/export data, the estimated intake was recalculated as 046 g kgbw 1 day 1; however, even at this higher level, coffee still contributed 22% of the daily intake..

Worse than simply their numbers, these patents are written in legalese, making them difficult to understand With the legal mess surrounding GIF, the best solution for developers is to use other formats Unlike JPEG, the patent situation with GIF is unlikely to be satisfactorily resolved

TABLE 2.1.2 Contribution of different meals and beverages to the daily intake of acrylamide by Swiss adults.a Meal category Breakfast Lunch Dinner Snacks Coffee Total

1044 (575)

127. China Standards (2000). SB 10338-12000, acid hydrolysed vegetable protein seasoning. http://www.chinagb.org/search/queryok.asp (accessed January 2007). 128. European Commission (2001). Commission Regulation (EC) No 466/2001 of 8 March 2001 setting maximum levels for certain contaminants in foodstuffs (OJ L 77 16.3.2001, p12). 129. World Trade Organization (WTO) (2001). Committee on Sanitary and Phytosanitary Measures Noti cation, Republic of Korea. Acid-hydrolyzed vegetable protein and soy sauce containing acid, G/SPS/N/KOR/106, 3 December 2001. http://www. ipfsaph.org/En/default.jsp (accessed January 2007). 130. World Trade Organization (WTO) (2001). Committee on Sanitary and Phytosanitary Measures Noti cation of Emergency Measures, Malaysia. Foods containing acid-hydrolyzed vegetable protein, G/SPS/N/MYS/10, 26 July 2001. http://www. ipfsaph.org/En/default.jsp (accessed January 2007). 131. D partement f d ral de l int rieur (DFI) (2006). Ordonnance du DFI du 26 juin 1995 sur les substances trang res et les composants dans les denr es alimentaires, RS 817.021.23 (DFI schedule on foreign substances and components in foodstuffs). DFI, Berne. http://www.admin.ch/ch/f/rs/c817_021_23.html (accessed January 2007). 132. World Trade Organization (WTO) (2002). Committee on Sanitary and Phytosanitary Measures Noti cation, Thailand. Vegetables and derived products, G/SPS/N/ THA/88, 26 March 2002. http://www.ipfsaph.org/En/default.jsp (accessed January 2007). 133. Committee on Food Chemicals Codex (1996). Food Chemicals Codex: First Supplement to Fourth Edition. Institute of Medicine of the National Academies, Washington DC. http://www.iom.edu/report.asp id=4590 (accessed January 2007).

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