evaluation of certain food additives - libdoc.who.int - World Health ...
evaluation of certain food additives - libdoc.who.int - World Health ...
evaluation of certain food additives - libdoc.who.int - World Health ...
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proportion <strong>of</strong> consumers in this group was higher. In all these studies, the<br />
beverages covered by Food Category 14.1.4 had provisions for cyclamates.<br />
In the one submission from Australia, three analyses were performed:<br />
1) The first assumed Codex GSFA maximum use levels in the low-joule<br />
(low-energy) version <strong>of</strong> all <strong>food</strong> categories, including beverages covered<br />
by Food Category 14.1.4 (where identified), and in the <strong>who</strong>le <strong>food</strong> category,<br />
for which the version was not identified. Individual body weights<br />
were used in the calculations.<br />
2) The second assumed the above was true, except for beverages covered by<br />
Food Category 14.1.4, for which it was assumed that cyclamates were<br />
added to all these beverages.<br />
3) The third assumed typical use levels for cyclamates in Australia for the<br />
low-joule versions <strong>of</strong> all <strong>food</strong> categories and the proposed GSFA use levels<br />
for low-joule beverages covered by Food Category 14.1.4.<br />
Dietary exposures were presented for all models for the baseline (i.e. no cyclamates<br />
in beverages covered by Food Category 14.1.4) and maximum use<br />
levels <strong>of</strong> 250, 500, 750 and 1000 mg/kg, as well as for a level <strong>of</strong> 350 mg/kg,<br />
which is the current permitted level <strong>of</strong> use in Australia and New Zealand for<br />
this category <strong>of</strong> beverages. The same <strong>food</strong> consumption data derived from<br />
individual records from the 1995 Australian National Nutrition Survey were<br />
used for estimating dietary exposures to cyclamates for all the models. For<br />
the <strong>who</strong>le population aged 2 years and over <strong>who</strong> were consumers <strong>of</strong> beverages<br />
covered by Food Category 14.1.4, mean consumption amounts ranged from<br />
375 to 560 g/day, and 90th-percentile amounts ranged from 625 to 1040 g/<br />
day. For children aged 2–6 years <strong>who</strong> were consumers <strong>of</strong> beverages covered<br />
by Food Category 14.1.4, mean consumption amounts ranged from 230 to<br />
420 g/day, and 90th-percentile amounts ranged from 320 to 900 g/day.<br />
For the first model, for the <strong>who</strong>le population aged 2 years and over, mean<br />
and 90th-percentile dietary exposures for consumers <strong>of</strong> products containing<br />
cyclamates were below the ADI <strong>of</strong> 0–11 mg/kg bw (25–30% <strong>of</strong> the ADI for<br />
mean consumers, 55–75% <strong>of</strong> the ADI for 90th-percentile consumers). For<br />
children aged 2–6 years, mean dietary exposures to cyclamates for consumers<br />
were also below the ADI (60–65% <strong>of</strong> the ADI). However, in this age group,<br />
dietary exposures to cyclamates exceeded the ADI at the 90th percentile <strong>of</strong><br />
exposure at baseline and for all optional levels <strong>of</strong> cyclamates in beverages<br />
covered by Food Category 14.1.4 (120–150% <strong>of</strong> the ADI). The higher dietary<br />
exposures expressed per kilogram body weight for young children compared<br />
with adults are to be expected, owing to relatively higher levels <strong>of</strong> consumption<br />
<strong>of</strong> <strong>food</strong> per kilogram body weight; additionally, members <strong>of</strong> this age<br />
group are relatively high consumers <strong>of</strong> fine bakery wares, juices and juice<br />
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