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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Administrative data

Endpoint:
chronic toxicity: oral
Type of information:
experimental study
Adequacy of study:
weight of evidence
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
data from handbook or collection of data

Data source

Reference
Reference Type:
review article or handbook
Title:
Bromide in drinking-water
Author:
WHO Guidelines for Drinking-water Quality
Year:
2009
Bibliographic source:
WHO

Materials and methods

Test guideline
Qualifier:
no guideline required
Principles of method if other than guideline:
Data from handbook
GLP compliance:
not specified

Test material

Constituent 1
Reference substance name:
Sodium bromide
EC Number:
231-599-9
EC Name:
Sodium bromide
Cas Number:
7647-15-6
Molecular formula:
BrNa
IUPAC Name:
sodium;bromide

Results and discussion

Effect levels

Key result
Dose descriptor:
other: ADI
Remarks:
Acceptable Daily Intake
Effect level:
0.4 mg/kg bw/day (nominal)
Based on:
test mat.
Sex:
not specified
Basis for effect level:
other: ADI is taken for the key result

Target system / organ toxicity

Key result
Critical effects observed:
not specified

Applicant's summary and conclusion

Conclusions:
As bromide ion is more hazardous than cupric ion, the toxicological data has been provided for bromide.

A conservative no-observed-effect level (NOEL) (for marginal effect within normal limits of EEGs in females at 9 mg/l) of 4 mg/kg bw per day gives an ADI of 0.4 mg/kg bw per day (EMEA, 1997; Sangster et al., 1986), including a safety factor of 10 for population diversity.
Executive summary:

The JMPR ADI of 0–1 mg/kg bw for bromide was set in 1966 and reaffirmed with new data in 1988. The typical daily dietary intake of bromide in the United States is 2–8 mg (Nielsen & Dunn, 2008) from grains, nuts and fish; the average bromide intake in the United Kingdom is reported as 8.4 mg/day. The intake of bromide from food would be smaller in bottle-fed infants. Bromide ion has a low degree of toxicity; thus, bromine is not of toxicological concern in nutrition. Limited findings suggest that bromide may be nutritionally beneficial; for example, insomnia exhibited by some haemodialysis patients

has been associated with bromide deficiency. A conservative no-observed-effect level (NOEL) (for marginal effect within normal limits of EEGs in females at 9 mg/l) of 4 mg/kg bw per day gives an ADI of 0.4 mg/kg bw per day (EMEA, 1997; Sangster et al., 1986), including a safety factor of 10 for population diversity. This yields an acceptable total daily intake of 24 mg/person per day, or a drinking-water equivalent value of 12 mg/l. Assuming a relative source contribution of 50%, the drinking-water value for a 60 - kg adult consuming 2 litres/day would be up to 6 mg/l; for a 10-kg child consuming 1 litre/day, the value would be up to 2 mg/l. These values apply specifically to inorganic bromide ion and not to organobromine compounds, which have individual guideline values.