INTERNATIONAL PROGRAMME ON CHEMICAL SAFETY WORLD HEALTH ORGANIZATION SAFETY EVALUATION OF CERTAIN FOOD ADDITIVES WHO FOOD ADDITIVES SERIES: 42 Prepared by the Fifty-first meeting of the Joint FAO/WHO Expert Committee on Food Additives (JECFA) World Health Organization, Geneva, 1999 IPCS - International Programme on Chemical Safety EVALUATION OF NATIONAL ASSESSMENTS OF INTAKE OF BUTYLATED HYDROXYANISOLE (BHA) First draft prepared by Janis Baines Australia New Zealand Food Authority, Canberra, Australia 1. INTRODUCTION The Committee assessed the intake of butylated hydroxyanisole (BHA), for which maximum limits have been proposed in a wide range of solid foods and water-based, flavoured, non-alcoholic drinks in the draft General Standard for Food Additives (GSFA) being developed by the Codex Committee on Food Additives and Contaminants (CCFAC). An ADI of 0-0.5 mg/kg bw has been allocated to BHA (Annex 1, reference 83). BHA is a food additive generally used as an antioxidant in products containing fats or oils and can be use in conjunction with butylated hydroxytoluene, tert-butylhydroquinone, and propyl gallate, for a synergistic combination of antioxidants. Information was provided by 10 countries: Australia, Brazil, China, Finland, France, Japan, New Zealand, Spain, the United Kingdom, and the United States. A combined assessment was provided by Australia and New Zealand (Aus-NZ). The assessments were based on data on poundage, household economic surveys or sales data, information from model diets, and/or individual dietary records. A summary of the data submitted is given in Table 1. Table 1. Summary of submissions on butylated hydroxyanisole Country Budget Poundage FBS/HES/ Model Individual dietary method data sales data diets records Australia-New Zealand X X X Brazil X X China X X X Finland X France X X Japan X Spain X X X United Kingdom X X X United States X X FBS, food balance sheet; HES, household economic survey; sales, retail stores 2. SCREENING OF BUTYLATED HYDROXYANISOLE BY THE BUDGET METHOD The Codex GSFA proposes to permit use of BHA in a wide range of solid foods and in water-based, flavoured drinks. Table 2 summarizes the calculations made by the budget method in each country, including the permitted patterns of BHA use, the proportion of solid foods and beverages likely to contain BHA, the maximum levels of BHA permitted, and a comparison of those levels with the theoretical maximum level calculated by the budget method for that country. The theoretical maximum level of use for BHA in solid foods was less than the national permitted maximum in the four countries that submitted data and was also less than the GSFA level of 1000 mg/kg. The submission from the United Kingdom noted that a previous assessment of intake of BHA by the budget method had indicated to CCFAC that detailed intake assessment was required. Spain and United States were the only countries in which use of BHA was reported to be permitted in beverages. As for solid food, the theoretical maximum level calculated by the budget method was less than the Spanish or GSFA permitted level of use. The United States did not submit detailed budget calculations, but it is likely that, as in Spain, at least 15% of the United States population consumes beverages that contain BHA. The theoretical maximum concentration would therefore be 17 mg/kg, which is lower than the 90 mg/kg permitted in beverage mixes in the United States. Detailed intake assessments are required for use of BHA in solid foods and beverages. 3. ASSESSMENTS OF INTAKE OF BUTYLATED HYDROXYANISOLE 3.1 Assessments based on data on poundage (disappearance) Estimates based on poundage data of the amount of BHA available per capita in five countries are shown in Table 3. The estimates are all below the ADI, with the exception of those for Spain, and vary widely, from 0.01 mg/kg bw per day (1% of the ADI) for China to 0.48 mg/kg bw per day (100% of the ADI) for Spain. The mean per capita intake of BHA appears to have declined from 0.03 to 0.01 mg/kg bw per day (from 6 to 2% of the ADI) in Finland between 1980 and 1995, but appears to have increased from 0.01 to 0.07 mg/kg bw per day (from 2 to 10% of the ADI) in the United States between 1987 and 1995. The estimated intake of 100% of the ADI in Spain is higher than in other countries, even for high consumers in the United States (0.14 mg/kg bw per day for those in the 90th percentile in 1995). These differences may be due to the reported use of BHA in both solid foods and beverages in Spain. Furthermore, the maximum permitted level in beverages (200 mg/kg) is higher than that in all other countries (90 mg/kg). It should be noted that the European Union does not permit use of BHA in beverages. The Spanish data may have been collated before the European Directive was agreed. Table 2. Estimates of theoretical maximum level for butylated hydroxyanisole (BHA) by the budget method Country % food or beverage National maximum GSFA maximum Theoretical maximum supply containing BHA level (mg/kg) levela (mg/kg) level (mg/kg) Australia-New Zealand 50% solid food 200 1000 solid food 40 Brazil 25% solid food 200 1000 solid food 80 China 20% solid food 200 1000 solid food 100 Spainb 5% solid food 400 solid food 1000 solid food 200 solid food 15% beverages 200 beverages 90 beverages 17 beverages GSFA, General Standard for Food Additives a Maximum use levels proposed are: 1000 mg/kg for 9.2.1, 'frozen fish, fish fillet and fish products, including molluscs, crustacea and echinoderms'; 90 mg/kg for 14.1.4.3 'concentrates (liquid or solid) for water-based flavoured drinks'. b Assumes that 50% BHA is used in solid food, 50% in beverages; current European Union directives do not permit use of BHA in beverages 3.2 Assessments based on data from food balance sheets and household economic surveys No countries reported use of data from food balance sheets to assess the intake of BHA. The submission of the United Kingdom notes that such data are expressed as raw commodities, and the percentages of the commodities that are processed and likely to contain the additive are not usually known. Four countries submitted data based on household surveys or sales data, in which maximum levels of use were assumed. The data are summarized in Table 4. Although high consumers generally cannot be identified from household economic surveys or sales data, the submission from France included estimates of the potential intake of consumers at the 90th and 95th percentiles on the basis of data for high consumer households. Estimates of the intake of BHA based on household economic surveys and sales data indicate that the potential intakes are all below the ADI, ranging from 0.02 mg/kg bw per day (3% of the ADI) in France to 0.25 mg/kg bw per day (50% of the ADI) in Spain. The higher estimate for Spain may reflect the use of BHA in both solid foods and beverages, whereas it is permitted for use only in solid foods in France and Brazil. 3.3 Assessments based on model diets Six countries submitted data based on model diets, details of which are summarized in Table 5. It is essential for the interpretation of estimates made with a model diet that the assumptions made in constructing each model diet be stated. The results cannot be compared directly because different assumptions were made. The model diets used in Aus-NZ and the United Kingdom were constructed to estimate the intake of a high consumer, assuming maximum additive concentrations. The model diet used in the United States was constructed to predict intake by a long-term consumer by using data on food consumption derived from food frequency tables for 1982-88 from the Market Research Corporation of America (MRCA) and average portion sizes from a three-day national food consumption survey conducted in 1987-88 by the US Department of Agriculture. Maximum additive concentrations were assumed. The Japanese model diet is different in that analytical values for food additive concentrations were used with data on national food consumption to derive an estimate of actual BHA intake for the average consumer. Table 5 summarizes the estimates based on model diets. The estimates based on the high-consumer models of Aus-NZ and the United Kingdom both exceed the ADI, with adult intakes of 2 mg/kg bw per day (400% of the ADI) in the United Kingdom, and 1.8 mg/kg bw per day (360% of the ADI) in Aus-NZ. The model used in the United Kingdom for children indicates that the intake of BHA by young children, 5.4 mg/kg bw per day (1000% of the ADI), tends to be higher than the intake of adults because of higher ratios of food consumption to body weight. A similar estimate, 4.8 mg/kg bw per day (950% of the ADI), was submitted by China for high consumers; however, this is an overestimate of intake even for a high consumer, as high levels of consumption of five food groups are summed to give a total BHA intake. In general, the estimates of intake in Aus-NZ, China, and the United Kingdom are higher than those from the long-term consumer model in the United States, as might be expected from the assumptions made. In the United States model, the estimated intakes are 0.38 mg/kg bw per day (76% of the ADI) for a mean consumer and 0.76 mg/kg bw per day (150% of the ADI) for a 90th percentile consumer. If GSFA levels of BHA are assumed, both the mean and high-consumer intakes of BHA exceed the ADI. The Japanese estimate for BHA intake from their total diet survey was much lower (0.003 mg/kg bw per day or 1% of the ADI) than the results from other model diets, because the concentrations of BHA were those actually measured -- for example, 0 for frozen fish, fats, and oils, 12 mg/kg for dried fish, 1 mg/kg for salted fish -- which were much lower than the maximum GSFA permitted levels of 200 mg/kg for frozen, dried, or salted fish, fats, and oils. In the absence of information on national levels of permitted use, BHA intake in Japan was estimated by assuming maximum GSFA levels and the reported Japanese food consumption data (the model assumed 200 mg/kg for all surveyed foods except 750 mg/kg in chewing gum). The revised estimate of intake for Japan was 0.11 mg/day (20% of the ADI). One useful aspect of the Aus-NZ and United Kingdom high-consumer models is that individual foods or food groups for which high consumption is likely to exceed the ADI can be identified. In the Aus-NZ model, assuming national additive use levels, high consumers of edible fat and fat emulsions may have BHA intakes that exceed the ADI (260% of the ADI). High consumers of dried mashed potato may have BHA intakes at the ADI (100%). In the United Kingdom model, high consumers of soup, processed vegetables, and comminuted meats may exceed the ADI (150, 140, and 130% of the ADI, respectively); however, this model diet assumed that the maximum concentration in fine bakery wares was 200 mg/kg, a level that actually applies to fine bakery ware mixes. Fine bakery wares would not be identified if the correct level of 25 mg/kg were used. If the proposed GSFA levels of BHA are substituted for national use levels in the models for the range of foods in which use is allowed, an additional list of foods is identified for which high consumption may result in BHA intakes that exceed the ADI. In the Aus-NZ model, such additional foods include cocoa and chocolate products, processed comminuted meat, fresh fish, and products including frozen fish, supplementary foods for dietary uses, and soups. Information on additional foods in which the concentration of BHA is at the GSFA level but not that of the European Union was not available for the United Kingdom model. Table 3. Estimates of intake of butylated hydroxyanisole (BHA) based on poundage data Country Date Assumptions Estimated intake of % ADIa Comments BHA (mg/kg bw per day) China ? Population, 1200 million 0.005 1 Used only in solid foods 70% consumes BHA Finland 1980 Population, 4.9 million 0.03 6 Used in 75% margarines, 25% oil 1994 Population, 5.1 million 0.01 2 dressings only Spain ? Not consumed by 15% of 0.48 100 Used in solid foods and beverages population < 3 years United Kingdom 1984-86 Population, 56 million 0.007 1 Used in limited number of solids foods only United States 1987 Population, 240 million Mean, 0.01 2 Used in solid foods and beverage 90th percentile consumers, 0.02 5 mixes 1995 Population, 260 million Mean, 0.07 10 90th percentile consumers, 0.14 30 100% consumes BHA Intake for 90th percentile consumers is twice the mean a JECFA ADI, 0-0.5 mg/kg bw Table 4. Estimates of intake of butylated hydroxyanisole (BHA) based on household economic surveys and sales data Country Date Survey Assumptions Estimated intake % ADIa of BHA (mg/kg bw per day) Brazil 1992-96 AC Nielsan Maximum national use levels for all foods, except chewing gumb 0.08 20 Brazil; Maximum national use levels, including chewing gum at 0.13 20 sales data GSFA level Population, 160 million 1984-94 Datamark; Maximum national use levels for all foods, except chewing gumb 0.09 20 mainly from Maximum national use levels, including chewing gum at 0.14 30 manufacturers GSFA level France ? Sales data Maximum European Union levels of use; mean corrected for 0.02 (corrected) 3 foods that never contain BHA in France (fats/oils) 0.08 (uncorrected) 20 Adjustment for catering outside the home: 90th percentile consumers 0.16 (uncorrected) 30 95th percentile consumers 0.2 (uncorrected) 40 Spain 1993 Household All foods in permitted groups contain BHA 0.25 50 survey Consumption inside and outside home No distinction for subgroups or rural/urban groups a JECFA ADI, 0-0.5 mg/kg bw b Assumed maximal level in final coconut and chewing gum products even though the use level in coconut is based on 60% fat content and that in chewing gum is based on 20% gum content, resulting in overestimates of BHA intake Table 5. Estimates of intake of butylated hydroxyanisole (BHA) based on model diets Country Date Survey Assumptions Type of model BHA intake %ADIa (mg/kg bw per day) Aus-NZ 1983 National, 24-h Two models: Aus-NZ /GSFA High consumerb recall; adults, -- maximum levels (Aus-NZ or GSFA) Aus-NZ permissions 1.78 360 25-64 years; -- 95th percentile high consumption level GSFA permissions 6.77 1400 sample, 6254; -- modified GSFA classification system body weight, 71 kg -- corrections for premixes/drink bases China 1992 National household survey, One model Average consumer 0.69 140 24-h recall; 30 provinces; -- maximum GSFA levels High consumer 4.77 950 sample, 91 818; body weight, 60 kg Japan 1994 Total diet/national One model: Japan Average consumer levels 0.003 1 nutrition intake survey; -- Analysed food additive concentrations GSFA permissions 0.11 20 body weight, 60 kg (zero values when not detected) (selected foods only) United 1986-87 National; 7-day weighed Three models: UK adult/child, GSFA High consumerb Kingdom record; adults, 16-64 years; -- maximum additive levels (EU) UK permissions/adult 2.02 400 body weight, 60 kg -- unit quantity diet (Codex model with UK permissions/child 5.38 1100 1992 National; 7-day weighed GSFA levels) Unit quantity diet/ 5.83 1200 record; children, 1.5-4.5 -- 97.5th percentile high consumption GSFA permissions years; body weight, 14.5 kg level (UK adult/child models) -- GSFA classification system United 1982-88 14-day menu obtained Two models/ US and GSFA Long-term consumer States from MRCA food -- maximum additive levels (US or GSFA) US permissions/means 0.38 80 frequency data (1982-87) -- 90th percentile high consumption level US permissions/90th 0.76 150 combined with portion twice mean consumption GSFA permissions/mean 0.94 190 sizes from USDA/NFCS -- all respondents are consumers GSFA permissions/90th 1.88 380 (1987-88); > 2 years; -- GSFA classification system (except body weight, 60 kg FSDU) -- corrections for premixes/drink bases Table 5 (continued) Aus-NZ, Australia-New Zealand; GSFA, General Standard for Food Additives; EU, European Union; MRCA, Market Research Corporation of America; USDA/NFCS, US Department of Agriculture/National Food Consumption Survey; FSDU, foods for special dietary uses a JECFA ADI, 0-0.5 mg/kg bw b Assumed to consume one food with potentially highest BHA intake from two major food groups at the 97.5th percentile (United Kingdom) or 95th percentile (Aus-NZ) and from one food with potentially highest BHA intake from each of the other major food groups at a mean level for all respondents 3.4 Assessments based on individual dietary records Estimates of the intake of BHA based on individual dietary records were submitted by three countries. Aus-NZ and France derived the mean and percentile intakes from individual estimates adjusted for individual body weight, while the United Kingdom did not. The assumptions made in deriving these estimates and the estimated intakes of BHA are summarized in Table 6. The estimates of mean intake of BHA based on individual dietary records and national use levels range from 0.03 to 0.39 mg/kg bw per day and are lower than the ADI for mean consumers in all countries and for high consumers in France and the United Kingdom. The lower reported intake in France (0.03 mg/kg bw per day) may be due to the exclusion of category 2 (edible fats and oils) in the estimates. There may be cause for concern for high consumers in Aus-NZ where the BHA intake is 0.91 mg/kg bw per day (130% of the ADI). Estimates of the intake of BHA based on GSFA levels and the range of foods in which use is allowed in Aus-NZ are higher than those based on national levels of use and exceed the ADI for both mean and high consumers. 4. EVALUATION OF ESTIMATES OF INTAKE OF BUTYLATED HYDROXYANISOLE In screening additives by the budget method, CCFAC identified BHA as an additive requiring detailed assessment. Inclusion of national proportions of food or beverages that may contain BHA in the budget method of screening did not alter this decision. Estimates of the intake of BHA were submitted by 10 countries. All of the approaches except that based on poundage were based on the assumption that the maximum permitted national levels represented actual additive levels, except in Japan where analytical data were used. Estimates based on maximum permitted additive levels result in overestimated actual intakes of additives. Estimates of per capita BHA intake based on poundage, household surveys, or sales data would be expected to predict lower intakes than those based on actual consumption, such as model diets and individual dietary records. In general, this was shown to be the case. Spain was the only country to submit intake estimates based on both poundage and household or sales data, the former being twice as high (100% of the ADI) as that based on sales data (50% of the ADI). The differences may be due to the fact that loss of additives in exported foods, non-food uses, and wastage are not taken into account in the poundage approach. Estimates of BHA intake based on high-consumer model diets and individual dietary records were submitted by Aus-NZ and the United Kingdom. In both cases, the estimates were two to three times higher than those based on individual dietary records of high consumers (95th percentile in Aus-NZ, 97.5th percentile in the United Kingdom). For these two submissions, the estimate based on individual dietary records was considered to be the most accurate. Table 6. Estimates of intake of butylated hydroxyanisole (BHA) based on individual records Country Date Survey Assumptions Type of model BHA intake %ADIa (mg/kg bw per day) Aus-NZ 1983 National survey; -- maximum additive levels (Aus-NZ or GSFA) Mean Aus-NZ 0.39 80 24-h recall; -- modified GSFA classification system Mean GSFA 0.91 180 adults, 25-64 years; -- maximum additive level within any one group sample, 6254 -- corrections for premixes/drink bases 95th Aus-NZ 1.3 260 -- reports 95th percentile consumption 95th GSFA 2.51 500 -- intakes adjusted for individual body weight -- all respondents are consumers France 1993-94 5-75 years; -- maximum additive levels (EU) but corrected Mean EU 0.07 14 sample, 1116 for foods that never contain BHA in France Corrected mean EU 0.03 6 (fats/oils) 90th EU 0.14 30 -- adjusted for catering outside the home 85th EU 0.16 30 -- intakes adjusted for individual body weight -- reports 90th, 95th percentile consumption -- reports by age group United 1986-87 National survey; -- maximum additive levels (EU) Mean EU 0.19 40 Kingdom 7-day weighed -- reports 97.5th percentile 97.5th EU 0.45 90 record; adults, -- GSFA classification system 16-64 years; -- assumes average body weight of 60 kg Aus-NZ, Australia-New Zealand; GSFA, General Standard for Food Additives; EU, European Union a JECFA ADI, 0-0.5 mg/kg bw The estimates based on individual records in Aus-NZ were higher than those for the United Kingdom, and both were higher than the estimates for France. In the Aus-NZ calculations, several GSFA food categories were combined, and the maximum permitted level was assigned to the wider food group. This tends to overestimate intake. The Aus-NZ estimates were also based on 24-h recall data, which is likely to lead to overestimated intakes in comparison with the seven-day record method used in the United Kingdom, because the range of reported daily food consumption levels tends to be wider. Some important differences in food consumption were seen, however, with much higher oil and fat consumption reported in Aus-NZ (mean, 130 g/day; 95th percentile, 450 g/day) than in the United Kingdom (mean, 23 g/day; 97.5th percentile, 58 g/day). These differences may be due to use of different assumptions about the BHA concentration in various classes of oils and fats: the Aus-NZ model included all fats and oils (all GSFA category 2 foods), consumed both as fats and oils and as ingredients in mixed foods. The United Kingdom model may have assumed that BHA was used in a more specific group of fats and oils, for example fat emulsions only. The estimates of mean national intake from the Chinese and United States model diets were in the same range as those based on individual dietary records in Aus-NZ and the United Kingdom. The estimated mean intakes for Japan, based on a model diet, and for France, based on individual records, were lower than those for other countries. All of the estimates for national mean intake of BHA, whether based on model diets or on individual dietary records, were lower than the ADI. The estimated intakes from individual records in Aus-NZ and from model diets in the United States indicate that high consumers of the whole diet might exceed the ADI. In addition, high consumers of individual foods may exceed the ADI, assuming maximum permitted additive levels in individual countries. Estimates derived by using GSFA additive levels grossly overestimate the actual intakes in any one country, because the GSFA is generally compiled by adopting the highest level of use of any one food category submitted to the CCFAC. The range of use specified in the GSFA is also much wider than in national standards. The best estimates from countries that submitted calculations based on GSFA levels in the range of foods in which it is allowed and model diets or individual records are summarized in Table 7. The mean BHA intakes in Aus-NZ (0.91 mg/kg bw per day) and the United States (0.94 mg/kg bw per day) are similar. The estimate for 95th percentile consumers in Aus-NZ is approximately three times higher than the mean intake in Aus-NZ and higher than the United States 90th percentile intake derived by multiplying the United States mean intake by two. These relationships between mean and 90th and 95th percentile intakes are generally recognized (UNEP/FAO/WHO, 1987). Table 7. Summary of estimates of intake of butylated hydroxyanisole (BHA) based on additive levels permitted within the General Standard for Food Additives Country Model Intake of BHA % ADIa (mg/kg bw per day) Aus-NZ Individual records, mean BHA intake 0.91 180 (all respondents are consumers) Individual records, 95th percentile BHA consumers 2.51 500 United Model diet, mean BHA intake 0.94 190 States (all respondents are consumers) Model diet, 90th percentile BHA consumers 1.88 380 a JECFA ADI, 0-0.5 mg/kg bw Estimates of intake based on GSFA maximum levels and the range of foods in which use of BHA is allowed indicate that the mean and the high consumer of BHA in Aus-NZ and the United States could exceed the ADI. 5. CONCLUSIONS AND RECOMMENDATIONS 5.1 National estimates of intake of butylated hydroxyanisole based on maximum limits specified in the General Standard for Food Additives Estimates of national mean intake based on maximum limits and the range of foods specified in the GSFA were available from two countries only; the mean intake estimates exceeded the ADI in these countries: 180% of the ADI for Aus-NZ and 190% of the ADI for the United States. 5.2 National estimates of intake of butylated hydroxyanisole based on national or European Union maximum limits All of the estimates of national mean intake by consumers of BHA were lower than the ADI of 0-0.5 mg/kg bw: 1% of the ADI for Japan to 80% of the ADI for Aus-NZ and the United States. These estimates were based either on model diets or on individual dietary records submitted by six countries, Aus-NZ, China, France, Japan, the United Kingdom, and the United States. Estimates of the intake of high consumers of BHA, based on food additive levels in national standards, exceed the ADI in some cases (30% of the ADI for France, 260% of the ADI for Aus-NZ); however, the available data were insufficient to estimate the number of high consumers or the magnitude or duration of intake at levels above the ADI over a lifetime. All of the estimates, with the exception of that from Japan, are based on the assumption that BHA is the only antioxidant in foods in which its use is permitted and that all such foods contain the additive at maximum permitted levels, thus tending to overestimate actual intake. Actual intakes of BHA depend on the relative proportions of BHA, butylated hydroxytoluene, tert-butylhydroquinone, and other antioxidants used in foods, the actual levels of use according to good manufacturing practice, and the the proportion of foods in any one category that contain the additive. 5.3 Recommendations to the Codex Committee on Food Additives and Contaminants The Committee identified foods and food groups that could potentially contribute to a high intake of BHA. The Codex Committee may wish to review the appropriate levels of BHA in the GSFA for category 2, 'edible fats and oils'; category 4.2.2.2, 'dried vegetables'; category 4.1.3, 'cocoa products'; category 8.3.1, 'processed comminuted meat'; category 9.2.1, 'frozen fish, fillets and products; category 12.5.1, 'ready to eat soup and broths'; and category 13.6, 'food supplements'. The Committee noted that intake estimates based on national maximum use levels of BHA were below the ADI, but those based on the maximum limits and range of foods specified in the GSFA exceeded it. The differences arise because the range of foods specified in the GSFA is wider and the proposed levels of use in specific food categories are generally higher than in national standards. 6. BIBLIOGRAPHY Australia New Zealand Food Authority (1997) Aus-NZ Food Standards Code, Canberra. Baines, J. Data sheets for Australia for TBHQ, BHA, BHT, sulfites, and benzoates. Personal communication. Australia-New Zealand Food Authority, Canberra, to J. Paakkanen, FAO, 5 January 1998. Chen Junshi. Food additive intake from China. Personal communication. Chinese Academy of Preventive Medicine, Beijing, to J. Paakkanen, FAO, 16 March 1998. Codex Committee on Food Additives and Contaminants (1997) Report of the Twenty-ninth Session of the Codex Committee on Food Additives and Contaminants, Rome, Food and Agriculture Organization of the United Nations (document ALINORM 97/12A, Appendix V). Codex Committee on Food Additives and Contaminants (1998) Consideration of the Codex General Standard for Food Additives: Proposed draft revised annex A at step 3. Request for comments and information. Rome, Food and Agriculture Organization of the United Nations (document CX/FAC 98/9). European Commission (1995) European Union Directive 95/2/CE, Brussels. FAO/WHO/UNEP (1987) Guidelines for the Study of Dietary Intake of Chemical Contaminants (WHO Publication No. 87), Geneva. Fisher, C.E. Dietary exposure in the United Kingdom to the five additives referred to JECFA by CCFAC. Personal communication. Joint Food Safety and Standards Group, London, to J. Paakkanen, FAO, 29 April 1998. Ishii, K. Use levels and intake estimates of certain food additives in Japan. Personal communication. Japan Food Additives Association, Tokyo, to J. Paakkanen, FAO, 10 May 1998. Ishiwata, H., Nishijima, M., Fukasawa, Y., Ito, Y. & Yamada, T. (1997) Evaluation of the contents of BHA, BHT, propylene glycol, and sodium saccharin in foods and estimation of daily intake based on the results of official inspection in Japan in fiscal year 1994. J. Food Hyg. Soc. Jpn, 39, 89-100. Ministry of Public Health (Spain) (1998) Calculation of certain food additives in Spain. Submitted to Food and Agriculture Organization of the United Nations. National Food Administration (Finland) (1998) Estimated intake of certain food additives in Finland. Submitted to FAO. Rulis, A.M. United States intake data on BHA, BHT, TBHQ, sulfites, and benzoates. Personal communication. Food and Drug Administration, Washington DC, to J. Paakkanen, FAO, 24 February 1998. Toledo, M.C.F. Brazilian intake estimates of BHA, BHT, and TBHQ. Personal communication. University of Campinas, to J. Paakkanen, FAO, 26 February 1998. United States Department of Agriculture (1996) Nationwide food consumption survey: 1989-91. Technical Information Service, Springfield, VA, United States. Verger, P. Estimation of the theoretical maximum intake of certain food additives in France. CNERNA, Paris. Submitted to J. Paakkanen, FAO, 16 March 1998.
For more information bht and tbhq, please get in touch with us!