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evaluation of certain food additives - libdoc.who.int - World Health ...

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The Committee had previously evaluated low-range sucrose esters <strong>of</strong> fatty<br />

acids, which principally include mono-, di- and tri-esters, at its thirteenth,<br />

seventeenth, twentieth, twenty-fourth, thirty-fifth, thirty-n<strong>int</strong>h, forty-fourth<br />

and forty-n<strong>int</strong>h meetings (Annex 1, references 19, 32, 41, 53, 88, 101, 116<br />

and 131). At the forty-n<strong>int</strong>h meeting, the Committee established a group ADI<br />

<strong>of</strong> 0–30 mg/kg bw for sucrose esters <strong>of</strong> fatty acids and sucroglycerides on the<br />

basis <strong>of</strong> potential laxative effects in humans.<br />

For the present <strong>evaluation</strong> <strong>of</strong> SOE type I and type II, the Committee considered<br />

the available data on the safety <strong>of</strong> SOE type I and type II in view <strong>of</strong> the<br />

Committee’s previous <strong>evaluation</strong> <strong>of</strong> low-range sucrose esters <strong>of</strong> fatty acids.<br />

Toxicological data<br />

The Committee considered studies <strong>of</strong> the absorption, distribution, metabolism<br />

and elimination (ADME) <strong>of</strong> components <strong>of</strong> SOE type I—i.e. tetra-,<br />

hexa- and octa-esters <strong>of</strong> fatty acids, each separately radiolabelled in both the<br />

fatty acid and sucrose moieties. These studies indicated that the tetra-, hexaand<br />

octa-esters <strong>of</strong> sucrose with stearic acid were very slowly hydrolysed prior<br />

to <strong>int</strong>estinal absorption <strong>of</strong> the hydrolysis products, but only the tetra-ester was<br />

hydrolysed and absorbed to any appreciable extent. These data were consistent<br />

with pharmacokinetic data on mono-, di- and tri-esters <strong>of</strong> sucrose with<br />

stearic and palmitic acids, which were reviewed at the forty-fourth meeting.<br />

Small amounts <strong>of</strong> mono-esters were absorbed <strong>int</strong>act, but the di- and tri-esters<br />

were not. Although specific ADME data for SOE type II were not available,<br />

their metabolic fate can be predicted by the demonstrated inverse relationship<br />

between hydrolysis and the degree <strong>of</strong> esterification <strong>of</strong> sucrose esters <strong>of</strong> fatty<br />

acids.<br />

Toxicological studies, including a 28-day range-finding study and a combined<br />

12-month toxicity and 2-year carcinogenicity study, were available for<br />

SOE type I fed to rats at dietary concentrations <strong>of</strong> up to 50 000 mg/kg (equal<br />

to 2370 mg/kg bw per day in males and 2800 mg/kg bw per day in females<br />

in the toxicity study; equal to 2120 mg/kg bw per day in males and 2420 mg/<br />

kg bw per day in females in the carcinogenicity study). In these studies, no<br />

significant toxicological or tumorigenic effects were reported. The NOEL<br />

from the 12-month toxicity study was 2370 mg/kg bw per day, the highest<br />

dose tested. The NOEL from the 2-year carcinogenicity study was 2120 mg/<br />

kg bw per day, the highest dose tested.<br />

No studies <strong>of</strong> reproductive or developmental toxicity were available for SOE<br />

type I or type II. However, in a two-generation reproductive and developmental<br />

toxicity study <strong>of</strong> sucrose polyester (a mixture <strong>of</strong> 8.2% hexa-, 33%<br />

hepta- and 58% octa-esters <strong>of</strong> edible-grade fatty acids with sucrose) fed to<br />

rats at up to 10% <strong>of</strong> their diet, no adverse effects on reproductive or developmental<br />

parameters were reported.<br />

47

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