Sucralose vs Brominated Flame Retardants: which is worse?
Quick answer: Brominated Flame Retardants carries the heavier risk profile. Sucralose is — in the EU and — in the US; Brominated Flame Retardants is — in the EU and — in the US.
| Property | Sucralose | Brominated Flame Retardants |
|---|---|---|
| EU status | — | — |
| US status | — | — |
| Risk level | — | — |
| Banned in | — | European Union (PBDEs banned since 2003 under RoHS; HBCD banned globally under Stockholm Convention 2013), United States (EPA banned penta- and octa-BDE in 2004 under TSCA; deca-BDE phase-out) |
| Restricted in | European Union (ADI 15 mg/kg body weight; required labeling), Australia, Canada | United States (EPA regulatory actions ongoing), Global Stockholm Convention (certain BFRs listed as POPs) |
| Category | additive | additive |
| Where it hides | — | — |
What is Sucralose?
Sucralose is a synthetic non-caloric sweetener made by selectively chlorinating three hydroxyl groups in sucrose (table sugar). Despite being derived from sugar, the chlorination makes it non-digestible: most passes through the body without being metabolized. It is approximately 600 times sweeter than sucrose.
What is Brominated Flame Retardants?
Brominated flame retardants (BFRs) are a class of synthetic chemicals added to consumer products and materials to reduce flammability. They include polybrominated diphenyl ethers (PBDEs), hexabromocyclododecane (HBCD), and others. While not direct food additives, they contaminate the food supply through environmental pathways and food packaging.
Documented risks
Sucralose: A 2023 study published in Nature Medicine found that sucralose-1,6-hexanediacid — a gut-derived metabolite of sucralose — enhanced T-cell immune activity in vitro. The researchers found that sucralose exposure in certain doses could potentially affect immune function. However, this was an early-stage study and its clinical implications for humans are not established. A 2021 Cell study found that sucralose and other non-nutritive sweeteners altered gut microbiome composition and glucose tolerance in human participants who were non-habitual sweetener users. The study found sucralose consumption was associated with glucose intolerance changes in some individuals, suggesting gut microbiome-mediated effects on metabolism. A 2016 study in the International Journal of Occupational and Environmental Health found sucralose consumption was associated with higher leukemia incidence in male mice at high lifetime doses. This finding prompted significant concern, though regulators noted the doses used far exceeded typical human intake. Chlorinated compounds: sucralose contains chlorine atoms in its structure. Critics have argued this makes it similar to organochlorine compounds, some of which are known carcinogens. Regulatory agencies have reviewed this and do not consider the chlorine in sucralose equivalent to organochlorine pollutants; the chlorinated positions are not metabolically active. However, high-temperature cooking with sucralose can generate chlorinated compounds. EFSA's 2017 re-evaluation concluded sucralose is safe and non-carcinogenic at its ADI of 15 mg/kg body weight. The FDA ADI of 5 mg/kg/day provides a substantial safety margin relative to typical consumer intake from Splenda use.
Brominated Flame Retardants: PBDEs and other BFRs are endocrine disruptors, neurodevelopmental toxicants, and probable carcinogens. They accumulate in human adipose tissue, breast milk, and blood. PBDEs were found in 100% of samples in multiple US population biomonitoring studies. US women have PBDE body burdens 10-100 times higher than European women, reflecting the US's historically heavy PBDE use before bans. Neurodevelopmental effects: multiple studies have associated prenatal PBDE exposure with lower IQ, attention deficits, and behavioral problems in children. A 2012 Environmental Health Perspectives study found inverse associations between PBDE cord blood levels and child IQ and behavioral outcomes. Thyroid disruption: BFRs structurally mimic thyroid hormones and compete with thyroid hormone binding proteins, disrupting the thyroid axis — critical for fetal brain development. Carcinogenicity: some PBDEs are associated with thyroid cancer risk in human studies. PBDEs enter the food supply primarily through fatty fish (salmon, tuna), meat, dairy, and some contaminated produce from biosolid-amended soils.
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