TY - JOUR
T1 - Risks to human and animal health from the presence of bromide in food and feed
AU - Bennekou, Susanne Hougaard
AU - Allende, Ana
AU - Bearth, Angela
AU - Casacuberta, Josep
AU - Castle, Laurence
AU - Coja, Tamara
AU - Crépet, Amélie
AU - Halldorsson, Thorhallur
AU - Hoogenboom, Laurentius (Ron)
AU - Knutsen, Helle
AU - Koutsoumanis, Konstantinos
AU - Lambré, Claude
AU - Nielsen, Søren
AU - Turck, Dominique
AU - Civera, Antonio Vicent
AU - Villa, Roberto
AU - Zorn, Holger
AU - Bampidis, Vasileios
AU - Castenmiller, Jacqueline
AU - Chagnon, Marie-Christine
AU - Cottrill, Bruce
AU - Darney, Keyvin
AU - Gropp, Jürgen
AU - Puente, Secundino Lopez
AU - Rose, Martin
AU - Vinceti, Marco
AU - Bastaki, Maria
AU - Gergelová, Petra
AU - Greco, Luna
AU - Innocenti, Matteo Lorenzo
AU - Janossy, Judit
AU - Lanzoni, Anna
AU - Terron, Andrea
AU - Benford, Diane
AU - EFSA Scientific Committee
PY - 2025
Y1 - 2025
N2 - The European Commission mandated EFSA to assess the toxicity of bromide, the existing maximum residue levels (MRLs), and possible transfer from feed into food of animal origin. The critical effects of bromide in experimental animals are on the thyroid and central nervous system. Changes in thyroid hormone homeostasis could result in neurodevelopmental toxicity, among other adverse effects. Changes in thyroid hormone concentrations and neurophysiological parameters have also been observed in experimental human studies, but the evidence was limited. Dose?response modelling of decreased blood thyroxine concentrations in rats resulted in a reference point of 40 mg/kg body weight (bw) per day. The Scientific Committee established a tolerable daily intake (TDI) of 0.4 mg/kg bw per day and an acute reference dose (ARfD) of 0.4 mg/kg bw per day to protect against adverse neurodevelopmental effects. The TDI value is supported by the results of experimental human studies with a NOAEL of 4 mg/kg bw per day and 10-fold interindividual variability. The TDI and ARfD are considered as conservative with 90% certainty. Insufficient evidence related to the toxicological effects of bromide was available for animals, with the exception of dogs. Therefore, the reference point of 40 mg/kg bw per day was extrapolated to maximum safe concentrations of bromide in complete feed for other animal species. Bromide can transfer from feed to food of animal origin, but, from the limited data, it was not possible to quantify the transfer rate. Monitoring data exceeded the current MRLs for some food commodities, generally with a low frequency. A conservative safety screening of the MRLs indicated that the TDI and ARfD are exceeded for some EU diets. Dietary exposure assessment for animals was not feasible due to insufficient data. The Scientific Committee recommends data be generated to allow robust dietary exposure assessments in the future, and data that support the risk assessment.
AB - The European Commission mandated EFSA to assess the toxicity of bromide, the existing maximum residue levels (MRLs), and possible transfer from feed into food of animal origin. The critical effects of bromide in experimental animals are on the thyroid and central nervous system. Changes in thyroid hormone homeostasis could result in neurodevelopmental toxicity, among other adverse effects. Changes in thyroid hormone concentrations and neurophysiological parameters have also been observed in experimental human studies, but the evidence was limited. Dose?response modelling of decreased blood thyroxine concentrations in rats resulted in a reference point of 40 mg/kg body weight (bw) per day. The Scientific Committee established a tolerable daily intake (TDI) of 0.4 mg/kg bw per day and an acute reference dose (ARfD) of 0.4 mg/kg bw per day to protect against adverse neurodevelopmental effects. The TDI value is supported by the results of experimental human studies with a NOAEL of 4 mg/kg bw per day and 10-fold interindividual variability. The TDI and ARfD are considered as conservative with 90% certainty. Insufficient evidence related to the toxicological effects of bromide was available for animals, with the exception of dogs. Therefore, the reference point of 40 mg/kg bw per day was extrapolated to maximum safe concentrations of bromide in complete feed for other animal species. Bromide can transfer from feed to food of animal origin, but, from the limited data, it was not possible to quantify the transfer rate. Monitoring data exceeded the current MRLs for some food commodities, generally with a low frequency. A conservative safety screening of the MRLs indicated that the TDI and ARfD are exceeded for some EU diets. Dietary exposure assessment for animals was not feasible due to insufficient data. The Scientific Committee recommends data be generated to allow robust dietary exposure assessments in the future, and data that support the risk assessment.
KW - animal health
KW - bromide
KW - feed
KW - health-based guidance value
KW - human health
KW - mode of action
KW - MRL
U2 - 10.2903/j.efsa.2025.9121
DO - 10.2903/j.efsa.2025.9121
M3 - Journal article
C2 - 39877303
VL - 23
JO - E F S A Journal
JF - E F S A Journal
SN - 1831-4732
IS - 1
M1 - e9121
ER -