| Literature DB >> 35770238 |
Maged Younes, Gabriele Aquilina, Laurence Castle, Karl-Heinz Engel, Paul Fowler, Maria Jose Frutos Fernandez, Ursula Gundert-Remy, Rainer Gürtler, Trine Husøy, Melania Manco, Wim Mennes, Peter Moldeus, Sabina Passamonti, Romina Shah, Ine Waalkens-Berendsen, Detlef Wölfle, Matthew Wright, Karlien Cheyns, Manuela Mirat, Ana Maria Rincon, Peter Fürst.
Abstract
Glycerol (E 422) was re-evaluated in 2017 by the former EFSA Panel on Food Additives and Nutrient sources added to Food (ANS). As a follow-up to that assessment, in this opinion, the Panel on Food Additives and Flavourings (FAF) addresses the data gaps identified to support an amendment of the EU specifications for E 422 in Commission Regulation (EU) No 231/2012. The Panel performed a risk assessment of undesirable impurities present in E 422. The Panel concluded that the maximum limits in the EU specifications for the four toxic elements (arsenic, lead, mercury and cadmium) should be lowered based on actual levels in the commercial food additive E 422. The Panel recommended setting a numerical limit value for acrolein in the specifications for E 422. The potential exposure to free 3-monochloropropanediol at the maximum limit of 0.1 mg/kg, as laid out in the specifications for E 422, does not give rise to a health concern. The Panel recommended to consider modifying the definition of E 422 in Commission Regulation (EU) No 231/2012 indicating that E 422 is obtained only from vegetable oils and fats and undergoes purification processes that involve distillation, and other clean up steps to obtain refined glycerol. Overall, the Panel concluded that the technical data provided support an amendment of the specifications for glycerol (E 422).Entities:
Keywords: CAS Registry Number 56‐85‐1; E 422; food additive; glycerin; glycerine; glycerol
Year: 2022 PMID: 35770238 PMCID: PMC9208908 DOI: 10.2903/j.efsa.2022.7353
Source DB: PubMed Journal: EFSA J ISSN: 1831-4732
Risk assessment for toxic elements
| (i) Considering the presence of toxic elements at the current limits of the EU specifications for E 422 (Commission Regulation (EU) No 231/2012) | ||||
|---|---|---|---|---|
| Exposure to E 422 (mg/kg bw per day) | MOE for Pb at 2 mg/kg | % of the TWI for Hg at 1 mg/kg | % of the TWI for Cd at 1 mg/kg | MOE for As at 3 mg/kg |
| 308(
| 0.81 | 54 | 86 | 0.32–8.7 |
| 460(
| 0.54 | 80 | 128 | 0.22–5.8 |
|
| ||||
|
|
|
|
|
|
| 308(
| 8.12 | 10.8 | 8.6 | 1.9–52 |
| 460(
| 5.43 | 16.1 | 12.9 | 1.3–35 |
|
| ||||
|
|
|
|
|
|
| 308(
| 8.12 | 2.70 | 17.2 | 4.87–130 |
| 460(
| 5.43 | 4.03 | 25.8 | 3.26–87.0 |
Highest exposure level among the different population groups (refined non‐brand‐loyal scenario – toddlers – mean (Table 2).
Highest exposure level among the different population groups (refined non‐brand‐loyal scenario – children – 95th percentile (Table 2).
Specifications for glycerol (E 422) according to Commission Regulation (EU) No 231/2012
| Commission Regulation (EU) No 231/2012 | |
|---|---|
| Assay | Content not less than 98% of glycerol on an anhydrous basis |
|
| Clear, colourless, hygroscopic syrupy liquid, with not more than a slight characteristic odour, which is neither harsh nor disagreeable |
|
| |
| Acrolein formation on heating | Heat a few drops of the sample in a test tube with about 0.5 g of potassium bisulfate. The characteristic pungent vapours of acrolein are evolved |
| Specific gravity (25/25°C) | Not less than 1.257 |
| Refractive index [n]D 20 | Between 1.471 and 1.474 |
|
| |
| Water | Not more than 5% (Karl Fischer method) |
| Sulfated ash | Not more than 0.01% determined at 800 ± 25°C |
| Butanetriols | Not more than 0.2% |
| Acrolein, glucose and ammonium compounds | Heat a mixture of 5 mL of glycerol and 5 mL of potassium hydroxide solution (1 in 10) at 60°C for 5 min. It neither becomes yellow nor emits an odour of ammonia |
| Fatty acids and esters | Not more than 0.1% calculated as butyric acid |
| Chlorinated compounds | Not more than 30 mg/kg (as chlorine) |
| 3‐monochloropropane‐1,2‐diol (3‐MCPD)) | Not more than 0.1 mg/kg |
| Arsenic | Not more than 3 mg/kg |
| Lead | Not more than 2 mg/kg |
| Mercury | Not more than 1 mg/kg |
| Cadmium | Not more than 1 mg/kg |
Summary of exposure to glycerol (E 422) from its use as a food additive considering food categories for which direct addition of glycerol is authorised (from Annex II to Regulation N°1333/2008) excluding alcoholic beverages (under FCS 14.2) in the refined non‐brand‐loyal exposure scenario, in six population groups (minimum–maximum across the dietary surveys in mg/kg bw per day) (EFSA ANS Panel, 2017)
| Infants (12 weeks–11 months) | Toddlers (12–35 months) | Children (3–9 years) | Adolescents (10–17 years) | Adults (18–64 years) | The elderly (≥ 65 years) | |
|---|---|---|---|---|---|---|
| • Mean | 6–100 | 89– | 112–240 | 74–162 | 50–100 | 53–77 |
| • 95th percentile | 153–266 | 261–418 | 222– | 149–298 | 110–197 | 98–147 |
Reference points/health‐based guidance values for impurities potentially present in E 422
| Impurity/constituent/HBGV/RP (ug/kg bw) | Basis/Reference |
|---|---|
| Lead (Pb)/0.5 (BMDL01) |
The reference point is based on a study demonstrating perturbation of intellectual development in children with the critical response size of 1 point reduction in IQ. The EFSA CONTAM Panel mentioned that a 1 point reduction in IQ is related to a 4.5% increase in the risk of failure to graduate from high school and that a 1 point reduction in IQ in children can be associated with a decrease of later productivity of about 2%. A risk cannot be excluded if the exposure exceeds the BMDL01 (MOE lower than 1) EFSA CONTAM Panel ( |
| Mercury (Hg)/4 (TWI) |
The HBGV was set using kidney weight changes in male rats as the pivotal effect. Based on the BMDL10 of 0.06 mg/kg bw per day, expressed as mercury, and an uncertainty factor of 100 to account for inter and intra species differences, with conversion to a weekly basis and rounding to one significant figure, a TWI for inorganic mercury of 4 μg/kg bw per week, expressed as mercury was established EFSA CONTAM Panel ( |
| Cadmium (Cd)/2.5 (TWI) |
The derivation of the reference point is based on a meta‐analysis to evaluate the dose‐response relationship between selected urinary cadmium and urinary beta‐2‐microglobulin as the biomarker of tubular damage recognised as the most useful biomarker in relation to tubular effects. A group‐based BMDL5 of 4 μg Cd/g creatinine for humans was derived. A chemical specific adjustment factor of 3.9 was applied to account for human variability in urinary cadmium within each dose‐subgroup in the analysis resulting in a reference point of 1.0 μg Cd per g creatinine. In order to remain below 1 μg Cd/g creatinine in urine in 95% of the population by age 50, the average daily dietary cadmium intake should not exceed 0.36 μg Cd/kg bw, corresponding to a weekly dietary intake of 2.5 μg Cd/kg bw EFSA CONTAM Panel ( |
|
Arsenic (As)/ 0.3–8 (BMDL01) |
The reference point is based on a range of benchmark dose lower confidence limit (BMDL01) values between 0.3 and 8 µg/kg bw per day identified for cancers of the lung, skin and bladder, as well as skin lesions. In general, the MOE should be at least 10,000 if the reference point is based on carcinogenicity in animal studies. However, as the BMDL for As is derived from human studies, an interspecies extrapolation factor (i.e. 10) is not needed EFSA CONTAM Panel (2009b); EFSA Scientific Committee ( |
| 3‐MCPD and 3‐MCPD fatty acid esters/2 (TDI) |
The HBGV is based on increased incidence of kidney tubular hyperplasia. BMD analysis using model averaging resulted in a BMDL10 of 0.20 mg/kg bw per day in male rats, which was selected as the reference point for renal effects. This reference point was considered to derive a group TDI of 2 μg/kg bw per day for 3‐MCPD and 3‐MCPD fatty acid esters and was considered protective also for effects on male fertility. EFSA CONTAM Panel ( |
| Acrolein/7.5 (provisional TC) |
A provisional tolerable concentration (TC) was developed on the basis of the NOEL for non‐neoplastic lesions in the gastrointestinal tract of rats
|
HBGV: Health‐based guidance value; RP: Reference point; BMDL01: benchmark dose (lower confidence limit); bw: body weight; TWI: Tolerable Weekly Intake; TDI: Tolerable Daily Intake; MOE: margin of exposure; 3‐MCPD: 3‐monochloropropanediol; TC: tolerable concentration.
Different scenarios for the potential exposure to toxic elements from the use of E 422
| Pb | Hg | Cd | As | |
|---|---|---|---|---|
|
| 0.02–0.14 | 0.005–0.19 | 0.02–0.1 | 0.02–0.43 |
|
| 2 | 1 | 1 | 3 |
|
| 0.2 | 0.2 | 0.1 | 0.5 |
|
| 0.2 | 0.05 | 0.2 | 0.2 |
Risk assessment for acrolein considering the presence of acrolein in E 422 at a level of 3 mg/kg (maximum amount level reported) or 5 mg/kg (10 times the reported LOQ)
| Exposure to E 422 (mg/kg bw per day) | % of the TC for acrolein (at 3 mg/kg in E 422) | % of the TC for acrolein (at 5 mg/kg in E 422) |
|---|---|---|
| 308(
| 12.3 | 20.5 |
| 460(
| 18.4 | 30.7 |
Highest exposure level among the different population groups (refined non‐brand‐loyal scenario – toddlers – mean (Table 2).
Highest exposure level among the different population groups (refined non‐brand‐loyal scenario – children – 95th percentile (Table 2).
Risk assessment for 3‐MCPD based on the current specification limit (0.1 mg/kg) for E 422 (Regulation EU no 231/2012)
| Exposure to E 422 (mg/kg bw per day) | % of the TDI for 3‐MCPD and fatty acid esters (expressed as 3‐MCPD) at 0.1 mg/kg |
|---|---|
| 308(
| 1.5 |
| 460(
| 2.3 |
Highest exposure level among the different population groups (refined non‐brand‐loyal scenario – toddlers – mean (Table 2).
Highest exposure level among the different population groups (refined non‐brand‐loyal scenario – children –95th percentile (Table 2).
Proposal for a revised version of the existing EU Specifications for glycerol (E 422)
| Commission Regulation (EU) No 231/2012 | Comment/justification for revision | |
|---|---|---|
|
| See Table | Definition to be amended to indicate that the food additive is obtained only from vegetable oils and fats and undergoes purification processes that involve distillation, and other clean up steps to obtain refined glycerol |
| Assay | See Table | Unchanged |
|
| See Table | Unchanged |
|
| See Table | Unchanged |
|
Infrared absorption spectrum Acrolein formation on heating | See Table | To be deleted* |
| Specific gravity (25/25 °C) | See Table | Unchanged |
| Refractive index [n]D20 | See Table | Unchanged |
|
| See Table | Unchanged |
| Water | See Table | Unchanged |
| Sulfated ash | See Table | Unchanged |
| Butanetriols | See Table | Unchanged |
| Acrolein | See Table | Maximum numerical limit to be included on the basis of the information provided and on the considerations of the Panel |
| Glucose and ammonium compounds | To be deleted** | |
| Fatty acids and esters | See Table | Unchanged |
| Chlorinated compounds | See Table | Unchanged |
| 3‐monochloropropane‐1,2‐diol (3‐MCPD) | Not more than 0.1 mg/kg | Unchanged |
| Arsenic | Not more than 3 mg/kg | Maximum limit to be lowered on the basis of the information provided and on the considerations of the Panel |
| Lead | Not more than 2 mg/kg | Maximum limit to be lowered on the basis of the information provided and on the considerations of the Panel |
| Mercury | Not more than 1 mg/kg | Maximum limit to be lowered on the basis of the information provided and on the considerations of the Panel |
| Cadmium | Not more than 1 mg/kg | Maximum limit to be lowered on the basis of the information provided and on the considerations of the Panel |
The Panel considered that a test for acrolein formation on heating as an identification of glycerol (Table 1) is obsolete considering that the content of glycerol in E 422 needs to be more than 98% and this identification and quantification have to be performed with an appropriate analytical method.
Because the test in the current EU specifications for the presence of acrolein, glucose and ammonium compounds is proposed to be replaced by another analytical method that allows to quantify acrolein (see Section 3.2.3).