| Literature DB >> 35795292 |
Maged Younes, Gabriele Aquilina, Gisela Degen, Karl-Heinz Engel, Paul J Fowler, Maria Jose Frutos Fernandez, Peter Fürst, Ursula Gundert-Remy, Rainer Gürtler, Trine Husøy, Melania Manco, Wim Mennes, Peter Moldeus, Sabina Passamonti, Romina Shah, Ine Waalkens-Berendsen, Matthew Wright, José Manuel Barat Baviera, David Gott, Jean-Charles Leblanc, Detlef Wölfle, Laura Ruggeri, Camilla Smeraldi, Alexandra Tard, Giorgia Vianello, Laurence Castle.
Abstract
The EFSA Panel on Food Additives and Flavourings (FAF) provides a scientific opinion on the safety of buffered vinegar as a new food additive. Buffered vinegar is a liquid or dried product prepared by adding sodium/potassium hydroxides (E 524 to E 525) and sodium/potassium carbonates (E 500 to E 501) to vinegar, compliant with European Standard EN 13188:2000 and exclusively obtained from an agricultural source origin (except wood/cellulose). The primary constituents of buffered vinegar are acetic acid and its salts. No biological or toxicological data obtained with the proposed food additive were submitted by the applicant as part of the dossier as, following oral ingestion, buffered vinegar dissociates into the acetic anion and acetate a natural constituent of the diet, and of the human body for which extensive data on their biological effects exist and for which EFSA in 2013 has previously concluded that the establishment of an acceptable daily intake (ADI) is not considered necessary. At the proposed maximum/typical use levels, the mean exposure to buffered vinegar from its use as a food additive expressed as acetic acid equivalents ranged from 8.9 mg/kg body weight (bw) per day in infants to 280.3 mg/kg bw per day in children. The 95th percentile of exposure to buffered vinegar ranged from 27.9 mg/kg bw per day in infants to 1,078 mg/kg bw per day in toddlers. The Panel concluded that there is no safety concern for the use of buffered vinegar as a food additive at the proposed maximum/typical use levels. The Panel could not conclude on the safety for the proposed uses at quantum satis as Group I food additive since the resulting exposure could not be estimated.Entities:
Keywords: acetic acid; buffered vinegar; food additive
Year: 2022 PMID: 35795292 PMCID: PMC9247865 DOI: 10.2903/j.efsa.2022.7351
Source DB: PubMed Journal: EFSA J ISSN: 1831-4732
Specifications for buffered vinegar, as proposed by the applicant (Documentation provided to EFSA n. 3)
|
| Buffered vinegar (liquid); buffered vinegar (powder) | |
|---|---|---|
|
| Buffered vinegar is a liquid or dried product prepared by adding buffering agents to vinegar. The buffering agents used are sodium/potassium hydroxides (E 524 to E 525) and sodium/potassium carbonates (E 500 to E 501). The vinegar is compliant with the European Standard EN 13188:2000 and is exclusively obtained from an agricultural source origin (except wood/cellulose). The primary constituents of buffered vinegar are acetic acid and its salts. | |
|
| Liquid: 15–40% (w/w) acetic acid equivalents | HPLC |
| Powder: 55–75% (w/w) acetic acid equivalents | ||
| 2 to 20% (w/w) free acetic acid | JECFA ( | |
|
| Liquid: colourless to brown viscous liquid | Internal method |
| Powder: white to creamish‐white crystalline powder | ||
|
| Liquid: pH 4.75–7.5 | Internal method |
| Powder: pH 4.75–6.75 (10% aqueous solution) | ||
|
| ||
| Total cations | Liquid: 3–30% total cations (NMT 10% sodium; NMT 30% potassium) | ICP |
| Powder: 20–40% total cations (NMT 30% sodium; NMT 40% potassium) | ||
| Water content | Powder: NMT 18% | Karl‐Fischer method |
| Ethanol | NMT 0.5% (w/w) | HS‐GC–MS |
| Arsenic | NMT 1 mg/kg | ICP |
| Lead | NMT 0.5 mg/kg | ICP |
| Mercury | NMT 0.5 mg/kg | ICP |
| Cadmium | NMT 0.5 mg/kg | ICP |
HS‐GC–MS: Headspace–gas chromatography–mass spectrometry; ICP: Inductively coupled plasma; NMT: no more than.
Acetic acid equivalents refer to the content of acetic acid and its salts, expressed as acetic acid.
Reference points/health‐based guidance value for toxic elements potentially present in the proposed food additive
| Element/HBGV/RP (μg/kg bw/d or/w) | Basis |
|---|---|
|
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, |
|
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, |
|
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 (B2M) 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/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, |
|
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, expressed as mercury was established (EFSA CONTAM Panel, |
Risk assessment for toxic elements using the specifications proposed by the applicant based on their lowest technologically achievable levels (documentation provided to EFSA n. 3)
| Exposure to proposed additive (mg/kg bw per day) | MOE for As at 1.0 mg/kg | MOE for Pb at 0.5 mg/kg | % of the TWI for Cd at 0.5 mg/kg | % of the TWI for Hg at 0.5 mg/kg |
|---|---|---|---|---|
| 280.3/1,583.6 | 0.189–5.1 | 0.63 | 221.7% | 138.6% |
Highest mean exposure from the proposed maximum/typical use level exposure assessment scenario (children population), being 280.3 mg/kg expressed as AAEs (using results from Table 5 calculated with SAS) and this corresponding to 1583.6 mg/kg of the proposed food additive in liquid form assuming an AAE value of 17.7%.
Proposed uses and maximum/typical use levels of buffered vinegar expressed as acetic acid equivalents (mg/kg)
| Food category number | Food category name | Restrictions/exceptions | Proposed maximum/typical use levels (expressed as acetic acid equivalents) (mg/kg) |
|---|---|---|---|
| 01.7.1 | Unripened cheese excluding products falling in category 16 | 7,500 | |
| 01.7.4 | Whey cheese | 7,500 | |
| 01.7.5 | Processed cheese | 7,500 | |
| 01.8 | Dairy analogues, including beverage whiteners | 3,000 | |
| 02.2 | Fat and oil emulsions mainly of type water‐in‐oil | 7,500 | |
| 04.1.2 | Peeled, cut and shredded fruits and vegetables | Legume fresh seeds only | 3,000 |
| 04.2 | Processed fruits and vegetables | Excluding dehydrated potato products and processed fruit products other than fruit preparations for fillings and/or flavouring | 3,000 |
| 04.2 | Processed fruits and vegetables | Only relishes | 7,500 |
| 04.2.5.4 | Nut butters and nut spreads | 3,000 | |
| 06.4 | Pasta | Excluding 6.4.2 Dry pasta | 7,500 |
| 07.1 | Bread and rolls | 7,500 | |
| 07.2 | Fine bakery wares | 7,500 | |
| 08.2 | Meat preparations as defined by Regulation (EC) No 853/2004 | 7,500 | |
| 08.3 | Meat products, including processed meat | 7,500 | |
| 09.2 | Processed fish and fishery products including molluscs and crustaceans | 7,500 | |
| 09.3 | Fish roe | 7,500 | |
| 10.2 | Processed eggs and egg products | 3,000 | |
| 12.2 | Herbs, spices, seasonings | 30,000 | |
| 12.5 | Soups and broth | 7,500 | |
| 12.6 | Sauces | 7,500 | |
| 12.7 | Salads and savoury‐based sandwich spreads | 7,500 | |
| 12.9 | Protein products | 7,500 | |
| 15.1 | Potato‐, cereal‐, flour‐ or starch‐based snacks | 3,000 | |
| 15.2 | Processed nuts | 3,000 | |
| 18 | Processed foods not covered by categories 1–17 excluding foods for infants and young children | 7,500 |
The Panel noted that for the proposed use in ‘relishes’, the most appropriate corresponding food category in Regulation (EC) No 1333/2008 would be ‘04.2.2. Fruit and vegetables in vinegar, oil, or brine’. The latter has been used for the exposure estimate performed by the Panel.
The Panel noted that the food category corresponding to the code 8.3 in Regulation (EC) No 1333/2008 is ‘Meat products’.
Population groups considered for the exposure estimates of buffered vinegar
| Population | Age range | Countries with food consumption surveys covering more than 1 day |
|---|---|---|
| Infants | From more than 12 weeks up to and including 11 months of age | Bulgaria, Cyprus, Denmark, Estonia, Finland, France, Germany, Italy, Latvia, Portugal, Slovenia |
| Toddlers | From 12 months up to and including 35 months of age | Belgium, Bulgaria, Cyprus, Denmark, Estonia, Finland, France, Germany, Hungary, Italy, Latvia, Netherlands, Portugal, Slovenia, Spain |
| Children | From 36 months up to and including 9 years of age | Austria, Belgium, Bulgaria, Cyprus, Czechia, Denmark, Estonia, Finland, France, Germany, Greece, Hungary, Italy, Latvia, Netherlands, Portugal, Spain, Sweden |
| Adolescents | From 10 years up to and including 17 years of age | Austria, Belgium, Cyprus, Czechia, Denmark, Estonia, Finland, France, Germany, Greece, Hungary, Italy, Latvia, Netherlands, Portugal, Romania, Slovenia, Spain, Sweden |
| Adults | From 18 years up to and including 64 years of age | Austria, Belgium, Croatia, Cyprus, Czechia, Denmark, Estonia, Finland, France, Germany, Greece, Hungary, Ireland, Italy, Latvia, Netherlands, Portugal, Romania, Slovenia, Spain, Sweden |
| The elderly | From 65 years of age and older | Austria, Belgium, Cyprus, Denmark, Estonia, Finland, France, Germany, Greece, Hungary, Ireland, Italy, Latvia, Netherlands, Portugal, Romania, Slovenia, Spain, Sweden |
The term ‘toddlers’ in the Comprehensive Database (EFSA, 2011) corresponds to ‘young children’ in Regulations (EC) No 1333/2008 and (EU) No 609/2013 (Regulation (EU) No 609/2013 of the European Parliament and of the Council of 12 June 2013 on food intended for infants and young children, food for special medical purposes and total diet replacement for weight control and repealing Council Directive 92/52/EEC, Commission Directives 96/8/EC, 1999/21/EC, 2006/125/EC and 2006/141/EC, Directive 2009/39/EC of the European Parliament and of the Council and Commission Regulations (EC) No 41/2009 and (EC) No f953/2009. OJ L 181, 29.6.2013, p. 35–56.).
The terms ‘children’ and ‘the elderly’ correspond, respectively, to ‘other children’ and the merge of ‘elderly’ and ‘very elderly’ in Comprehensive Database (EFSA, 2011).
Summary of dietary exposure to buffered vinegar from its proposed maximum/typical use levels as a food additive in six population groups, estimated with FAIM (minimum–maximum across the dietary surveys in mg/kg bw per day expressed as acetic acid equivalents)
| 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 | 32.1–214.9 | 85.7–323.2 | 91.5–336.2 | 39.2–165.3 | 36.1–98.0 | 36.4–73.4 |
| 95th percentile | 100.7–629.2 | 147.0–1,142.7 | 154.7–1,044.3 | 66.8–520.8 | 63.8–347.0 | 60.5–261.0 |
Mean values considered for the safety assessment of the proposed food additive.
Summary of dietary exposure to buffered vinegar from its use as a food additive in the proposed maximum/typical level exposure assessment scenario, in six population groups (minimum–maximum across the dietary surveys in mg/kg bw per day)
| 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 | 8.9–145.9 | 31.8–263.4 | 57.2–280.3 | 22.8–138.1 | 22.5–81.4 | 18.8–59.9 |
| 95th percentile | 27.9–450.5 | 86.9–1,078.2 | 109.2–951.9 | 42.2–499.6 | 43.0–333.9 | 36.0–253.1 |
Qualitative evaluation of influence of uncertainties on the dietary exposure estimate
| Sources of uncertainties | Direction |
|---|---|
| Consumption data: different methodologies/representativeness/underreporting/misreporting/no portion size standard | +/− |
| Methodology used to estimate high percentiles (95th) long‐term (chronic) exposure based on data from food consumption surveys covering only a few days | + |
| Correspondence of proposed use levels to the food items in the EFSA Comprehensive Database: uncertainties to which types of food the levels refer to | +/− |
| Uncertainty in possible national differences in use levels of food categories | +/− |
|
Concentration data: Proposed maximum/typical use levels considered applicable to all foods within the entire food category, whereas most probably not all food belonging to a proposed food categories will contain buffered vinegar as a food additive |
+ |
+, uncertainty with potential to cause overestimation of exposure; −, uncertainty with potential to cause underestimation of exposure.
Risk assessment for toxic elements using the analytical data provided by the applicant (documentation provided to EFSA n. 1)
| Exposure to proposed additive (mg/kg bw/day) | MOE for As at 0.05 mg/kg | MOE for Pb at 0.05 mg/kg | % of the TWI for Cd at 0.05 mg/kg | % of the TWI for Hg at 0.05 mg/kg |
|---|---|---|---|---|
| 280.3/1,583.6 | 3.789–101.0 | 6.31 | 22.2% | 13.9% |
Highest mean exposure from the proposed maximum/typical use level exposure assessment scenario (children population), being 280.3 mg/kg expressed as AAEs (using results from Table 5 calculated with SAS) and this corresponding to 1,583.6 mg/kg of the proposed food additive in liquid form assuming an AAE value of 17.7%.