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EC number: 231-599-9 | CAS number: 7647-15-6
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Endpoint summary
Administrative data
Key value for chemical safety assessment
Effects on fertility
Link to relevant study records
- Endpoint:
- three-generation reproductive toxicity
- Remarks:
- based on test type (migrated information)
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study well documented, meets generally accepted scientific principles, acceptable for assessment.
- Principles of method if other than guideline:
- Male and female Wistar rats received 0, 75, 300, 1200, 4800 and 19200 mg NaBr in the diet during three successive generations. The study was designated to evaluate the reproductive and developmental effects of sodium bromide in multiple generations as well as the effect on the thyroid function in the parental animals.
- GLP compliance:
- not specified
- Limit test:
- no
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Age at study initiation: 4 months. - Route of administration:
- oral: feed
- Vehicle:
- unchanged (no vehicle)
- Details on mating procedure:
- Male rats of proven fertility were mated with females.
- Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- Three generations.
- Frequency of treatment:
- Daily.
- Details on study schedule:
- In three successive generations, at least two litters per female rat were raised. In the first generation a third litter was raised for the investigation of the transplacental transport of bromide. Furthermore, an additional litter was bred with parent animals of the highest dose group which were changed to the control diet in order to investigate the reversibility of the observed effects.
- Remarks:
- Doses / Concentrations:
0, 75, 300, 1200, 4800 and 19200 mg NaBr/kg diet.
Basis:
nominal in diet - No. of animals per sex per dose:
- Males: 9-10 animals/dose group.
Females: 7-11 animals/dose group (F0); 14-19 animals/dose group (F1); 10 animals/dose group (F2). - Control animals:
- yes, plain diet
- Details on study design:
- Because of the diminished fertility in the two highest dose groups, second and third generations were bred only from the groups dosed with sodium bromide up to 1200 mg/kg diet.
- Positive control:
- None.
- Parental animals: Observations and examinations:
- CLINICAL OBSERVATIONS: Yes.
BODY WEIGHT: Yes.
OTHER:
HAEMATOLOGY: haematological examinations were carried out 3 weeks before each mating and directly after the weaning of the last litter.
THYROID FUNCTION: the thyroid hormone (T4) concentration in serum was determined in parent animals of the F0 generation. - Oestrous cyclicity (parental animals):
- No data.
- Sperm parameters (parental animals):
- No data.
- Litter observations:
- PARAMETERS EXAMINED
The following parameters were examined: number and sex of pups, viability, presence of gross anomalies, body weight and bromide ion levels in foetal kidneys. - Postmortem examinations (parental animals):
- ORGAN WEIGHTS
The tissues indicated in Table 2 were weighed: adrenals, thyroid, pituitary, ovaries, uterus, testes, prostate. - Postmortem examinations (offspring):
- ORGAN WEIGHTS
The tissues indicated in Table 2 were weighed: adrenals, thyroid, pituitary, ovaries, uterus, testes, prostate. - Statistics:
- No data.
- Reproductive indices:
- Fertility index (no. of pregnancies x 100/no. of matings).
- Offspring viability indices:
- Viability index (no. of pups alive at day 5 x 100/no. of pups born alive); Lactation index (no. of pups alive at day 21 x 100/no. of pups alive at day 5).
- Clinical signs:
- effects observed, treatment-related
- Body weight and weight changes:
- no effects observed
- Food consumption and compound intake (if feeding study):
- no effects observed
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Histopathological findings: non-neoplastic:
- not examined
- Other effects:
- not examined
- Reproductive function: oestrous cycle:
- not examined
- Reproductive function: sperm measures:
- not examined
- Reproductive performance:
- effects observed, treatment-related
- Description (incidence and severity):
- (≥ 4,800 mg/kg)
- Dose descriptor:
- NOAEL
- Remarks:
- (reproductive)
- Effect level:
- 1 200 mg/kg diet
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: Based on fertility index (equivalent to 120 and 60 mg/kg b.w./day for young and older rats, respectively).
- Dose descriptor:
- NOAEL
- Remarks:
- (developmental)
- Effect level:
- 1 200 mg/kg diet
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: Based on viability index (equivalent to 120 and 60 mg/kg b.w./day for young and older rats, respectively).
- Remarks on result:
- other: Generation: F1, F2 (migrated information)
- Dose descriptor:
- NOAEL
- Remarks:
- (systemic)
- Effect level:
- 300 mg/kg diet
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: Based on thyroid function (equivalent to 30 and 15 mg/kg b.w./day for young and older rats, respectively).
- Clinical signs:
- no effects observed
- Mortality / viability:
- mortality observed, treatment-related
- Description (incidence and severity):
- (≥ 4,800 mg/kg)
- Body weight and weight changes:
- no effects observed
- Sexual maturation:
- not specified
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- no effects observed
- Histopathological findings:
- not examined
- Reproductive effects observed:
- not specified
- Conclusions:
- The NOAEL for reproductive and developmental toxicity was determined to be 1200 mg/kg diet (equivalent to 120 and 60 mg/kg bw/d for young and older rats, respectively).
- Executive summary:
A three-generation reproduction study was performed with the test substance sodium bromide on Wistar rats at dietary concentrations of 0, 75, 300, 1200, 4800 and 19,200 mg NaBr/kg diet. For the performance of the experiment, male rats of proven fertility were mated with females for the first time at the age of 4 months. In three successive generations, at least two litters per female rat were raised. Besides, in the first generation a third litter was raised for the investigation of the transplacental transport of bromide and an additional litter was bred with parent animals of the highest dose group which were changed to the control diet in order to investigate the reversibility of the observed effects. Fertility index, viability and lactation indices were evaluated for each generation. Haematological examinations were made and the thyroid function was evaluated. Body- and organ-weights were also determined. The bromide concentration determination in foetal kidneys of the third litter of the first generation showed that foetuses in utero were indeed exposed to bromide. Body- and organ-weight determinations did not reveal a clear pattern of dose-related effects in the successive generations. The fertility was found to be nil in the 19,200 -mg group and was markedly reduced in the 4800 -mg group. Nevertheless, the decrease in fertility appeared to be reversible upon bromide withdrawal. In the 4800 -mg group also the viability of the offspring was lower than in the other groups. Macroscopic examination of all pups provided no evidence of anomalies. Besides the effects on fertility and viability, the most prominent effect observed in the present study was a decrease in thyroid hormone (T4) concentration in the serum of the parent animals of the P -generation. This finding is indicative of an inhibitory action of bromide on the synthesis of thyroid hormones. On the basis of the effect of sodium bromide on the thyroid function, a no-effect level of 300 mg/kg diet was determined (equivalent to 30 and 15 mg/kg bw/d for young and older rats, respectively). On the basis on the fertility and viability indices, the NOAEL for reproductive and developmental toxicity was determined to be 1200 mg/kg diet (equivalent to 120 and 60 mg/kg bw/d for young and older rats, respectively).
Reference
Body weight determinations did not reveal a clear pattern of dose-related effects.
REPRODUCTIVE PERFORMANCE (PARENTAL ANIMALS)
The fertility was nil in the 19,200-mg group and was markedly reduced in the 4,800-mg group. The reversibility of the effects on reproduction was studied in parent animals fed a diet containing 19,200 mg NaBr/kg for 7 months followed by a control diet for 3 months before mating. The results were as follows: fertility index, 62%; viability index, 61%; lactation index, 90%. Although the viability was lower than in the control and lower dose groups, the fertility index and lactation index were similar.
ORGAN WEIGHTS (PARENTAL ANIMALS)
Organ-weight determinations did not reveal a clear pattern of dose-related effects in the successive generations. Only the adrenals of the females of the F0-generation showed a dose-dependent decrease in relative weight.
OTHER FINDINGS (PARENTAL ANIMALS)
HAEMATOLOGY: it was found a dose-related increase of the bromide levels in plasma, placenta and kidneys.
THYROID FUNCTION: a decrease in thyroid hormone (T4) concentration was found in the serum of the parent animals of the P-generation. The no-effect level for thyroid function was fixed at 300 mg/kg. This finding is indicative of an inhibitory action of bromide on the synthesis of thyroid hormones.
In the 4,800-mg group the viability of the offspring was lower than in the other groups. In this group, the viability of the young was greater in the second litter than in the first. Furthermore, during lactation of the first litter all of the young alive at day 5 died before day 21. In the second litter of this group, however, all animals alive at day 5 were still alive at day 21.
BODY WEIGHT (OFFSPRING)
Body weight determinations did not reveal a clear pattern of dose-related effects.
ORGAN WEIGHTS (OFFSPRING)
Organ-weight determinations given in Table 2 did not reveal a clear pattern of dose-related effects.
BROMIDE CONCENTRATIONS
The bromide levels in foetal kidneys demonstrate that foetuses in utero were exposed to bromide, since the concentration of bromide in the kidneys corresponding dams and foetuses is almost equal.
Table 1. Breeding results in reproduction study on sodium bromide fed to rats at dietary levels up to 19200 mg/kg.
|
Values for groups fed NaBr at dietary levels (mg/kg) of: |
|||||
Generation |
0 |
75 |
300 |
1200 |
4800 |
19200 |
|
Fertility index* |
|||||
F0 |
70 |
70 |
72 |
65 |
25 |
0 |
F1 |
62 |
54 |
44 |
53 |
- |
- |
F2 |
52 |
67 |
80 |
45 |
- |
- |
|
Viability index* |
|||||
F0 |
90 |
98 |
96 |
92 |
32, 61+ |
- |
F1 |
92 |
88 |
80 |
97 |
- |
- |
F2 |
96 |
98 |
93 |
98 |
- |
- |
|
Lactation index* |
|||||
F0 |
95 |
96 |
95 |
94 |
0, 100+ |
- |
F1 |
93 |
85 |
72 |
80 |
- |
- |
F2 |
99 |
99 |
99 |
99 |
- |
- |
|
Mean body weight at day 21 |
|||||
F0 |
40 |
45 |
43 |
43 |
-, 38+ |
- |
F1 |
41 |
43 |
40 |
38 |
- |
- |
F2 |
36 |
38 |
38 |
36 |
- |
- |
*Fertility index = no. of pregnancies x 100/no. of matings; viability index = no. of pups alive at day 5 × 100/no. of pups born alive; lactation index = no. of pups alive at day 21 × 100/no. of pups alive at day 5.
+ Data are given separately for first and second litter.
Table 2. Reproduction study in rats fed sodium bromide at dietary levels up to 4800 mg/kg: mean body weights and relative organ weights determined at the end of each generation.
Generation |
Parameter+ |
|
Values for groups fed NaBr at dietary levels (mg/kg) of: |
||||
0 |
75 |
300 |
1200 |
4800 |
|||
Males |
|||||||
F0 |
|
No./group… |
9 |
9 |
9 |
10 |
10 |
Body weight (g) |
|
422 |
398 |
383 |
391 |
362 |
|
Adrenals |
|
0.011 |
0.011 |
0.011 |
0.011 |
0.012 |
|
Thyroid |
|
0.0060 |
0.0057 |
0.0056 |
0.0060 |
0.0060 |
|
Pituitary |
|
0.0029 |
0.0029 |
0.0029 |
0.0030 |
0.0033 |
|
Testes |
|
0.680 |
0.745 |
0.776** |
0.744 |
0.712 |
|
Prostate |
|
0.119 |
0.130 |
0.121 |
0.135 |
0.134 |
|
F1 |
|
No./group… |
10 |
10 |
10 |
10 |
- |
Body weight (g) |
|
409 |
391 |
388 |
395 |
- |
|
Adrenals |
|
0.010 |
0.010 |
0.011 |
0.012 |
- |
|
Thyroid |
|
0.0063 |
0.0064 |
0.0060 |
0.0067 |
- |
|
Pituitary |
|
0.0026 |
0.0026 |
0.0027 |
0.0028 |
- |
|
Testes |
|
0.771 |
0.759 |
0.769 |
0.763 |
- |
|
Prostate |
|
0.077 |
0.093 |
0.093 |
0.102* |
- |
|
F2 |
|
No./group… |
10 |
10 |
10 |
10 |
- |
Body weight (g) |
|
438 |
373** |
397** |
378** |
- |
|
Adrenals |
|
0.010 |
0.010 |
0.009 |
0.010 |
- |
|
Thyroid |
|
0.0076 |
0.0074 |
0.0079 |
0.0081 |
- |
|
Pituitary |
|
0.0032 |
0.0031 |
0.0027** |
0.0029 |
- |
|
Testes |
|
0.787 |
0.821 |
0.679 |
0.793 |
- |
|
Prostate |
|
0.103 |
0.102 |
0.109 |
0.104 |
- |
|
Females |
|||||||
F0 |
|
No./group… |
7 |
11 |
9 |
12 |
11 |
Body weight (g) |
|
254 |
256 |
249 |
243 |
249 |
|
Adrenals |
|
0.020 |
0.019 |
0.019 |
0.017* |
0.017** |
|
Thyroid |
|
0.0062 |
0.0066 |
0.0066 |
0.0073 |
0.0073 |
|
Pituitary |
|
0.0056 |
0.0055 |
0.0052 |
0.0052 |
0.0046 |
|
Ovaries |
|
0.022 |
0.021 |
0.022 |
0.025 |
0.024 |
|
Uterus |
|
0.171 |
0.166 |
0.180 |
0.150 |
0.143 |
|
F1 |
|
No./group… |
19 |
15 |
14 |
16 |
- |
Body weight (g) |
|
244 |
254 |
252 |
241 |
- |
|
Adrenals |
|
0.018 |
0.018 |
0.017 |
0.017 |
- |
|
Thyroid |
|
0.0073 |
0.0070 |
0.0074 |
0.0083 |
- |
|
Pituitary |
|
0.0047 |
0.0052 |
0.0049 |
0.0053* |
- |
|
Ovaries |
|
0.026 |
0.029 |
0.027 |
0.027 |
- |
|
Uterus |
|
0.167 |
0.159 |
0.150 |
0.140* |
- |
|
F2 |
|
No./group… |
10 |
10 |
10 |
10 |
- |
Body weight (g) |
|
267 |
244 |
259 |
241** |
- |
|
Adrenals |
|
0.019 |
0.018 |
0.017 |
0.018 |
- |
|
Thyroid |
|
0.0096 |
0.0083 |
0.0094 |
0.0103 |
- |
|
Pituitary |
|
0.0053 |
0.0048 |
0.0050 |
0.0056 |
- |
|
Ovaries |
|
0.027 |
0.024 |
0.027 |
0.027 |
- |
|
Uterus |
|
0.188 |
0.160 |
0.179 |
0.164 |
- |
+All organ weights are expressed in g/100 g body weight.
Asterisks indicate means differing significantly from that of the corresponding control group: *-0.01 ≤ p < 0.05; **-0.001 ≤ p < 0.01.
Table 3. Bromide concentration (corrected for control values) in plasma, tissues and 20 -day foetuses of female rats fed sodium bromide at 75 -4800 mg/kg diet for 7 months.
Dietary concentration of NaBr (mg/kg) |
Maternal levels of Br- |
Br- in foetal kidneys (mmol/kg) |
||
Plasma (mmol/litre) |
Placenta (mmol/kg) |
Kidneys (mmol/kg) |
||
75 |
0.5 ± 0.1 |
0.4 ± 0.1 |
0.3 ± 0.1 |
0.3 ± 0.1 |
300 |
2.2 ± 0.1 |
1.4 ± 0.1 |
1.4 ± 0.3 |
0.9 ± 0.1 |
1200 |
7.8 ± 0.9 |
6.3 ± 1.5 |
4.4 ± 1.1 |
3.2 ± 0.8 |
4800 |
27.6 ± 2.8 |
16.7 ± 1.5 |
15.3 ± 1.4 |
11.0 ± 0.6 |
Values are means ±SD for groups of seven animals.
Effect levels:
The effect levels were reported as Concentration of the substance in feed (mg/kg diet). In order to express the dose levels as mg/kg Body Weight Per Day, a conversion factor of 0.1 for young rats and 0.05 for older rats were used (in accordance with the OECD Environment, Health and Safety Publications Series on Testing and Assessment No.51, Paris, 2006).
Effect on fertility: via oral route
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- NOAEL
- 120 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
- Quality of whole database:
- Key study with Klimish = 2: Study well documented, meets generally accepted scientific principles, acceptable for assessment.
Effect on fertility: via inhalation route
- Endpoint conclusion:
- no study available
Effect on fertility: via dermal route
- Endpoint conclusion:
- no study available
Additional information
Key study: A three-generation reproduction study was performed with the test substance sodium bromide on Wistar rats at dietary concentrations of 0, 75, 300, 1200, 4800 and 19,200 mg NaBr/kg diet. For the performance of the experiment, male rats of proven fertility were mated with females for the first time at the age of 4 months. In three successive generations, at least two litters per female rat were raised. Besides, in the first generation a third litter was raised for the investigation of the transplacental transport of bromide and an additional litter was bred with parent animals of the highest dose group which were changed to the control diet in order to investigate the reversibility of the observed effects. Fertility index, viability and lactation indices were evaluated for each generation. Haematological examinations were made and the thyroid function was evaluated. Body- and organ-weights were also determined. The bromide concentration determination in foetal kidneys of the third litter of the first generation showed that foetuses in utero were indeed exposed to bromide. Body- and organ-weight determinations did not reveal a clear pattern of dose-related effects in the successive generations. The fertility was found to be nil in the 19,200 -mg group and was markedly reduced in the 4800 -mg group. Nevertheless, the decrease in fertility appeared to be reversible upon bromide withdrawal. In the 4800 -mg group also the viability of the offspring was lower than in the other groups. Macroscopic examination of all pups provided no evidence of anomalies. Besides the effects on fertility and viability, the most prominent effect observed in the present study was a decrease in thyroid hormone (T4) concentration in the serum of the parent animals of the P -generation. This finding is indicative of an inhibitory action of bromide on the synthesis of thyroid hormones. On the basis of the effect of sodium bromide on the thyroid function, a no-effect level of 300 mg/kg diet was determined (equivalent to 30 and 15 mg/kg bw/d for young and older rats, respectively). On the basis on the fertility and viability indices, the NOAEL for reproductive and developmental toxicity was determined to be 1200 mg/kg diet (equivalent to 120 and 60 mg/kg bw/d for young and older rats, respectively).
Short description of key information:
Key study: Study well documented, meets generally accepted scientific principles, acceptable for assessment. The NOAEL for reproductive and developmental toxicity was determined to be 1200 mg/kg diet (equivalent to 120 and 60 mg/kg bw/d for young and older rats, respectively).
Justification for selection of Effect on fertility via oral route:
Only one fertility study is available.
Effects on developmental toxicity
Description of key information
Key study: Study well documented, meets generally accepted scientific principles, acceptable for assessment. The LOAEL for maternal toxicity and teratogenicity was established to be 847.13 mg Br-/kg bw/day (equivalent to 1086.88 mg NaBr/kg bw/day).
Link to relevant study records
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study well documented, meets generally accepted scientific principles, acceptable for assessment.
- Principles of method if other than guideline:
- Female Wistar rats were mated and dosed with a high and a low dose of sodium bromide in their drinking water from 2nd to the 28th day postpartum.
- GLP compliance:
- not specified
- Limit test:
- no
- Species:
- rat
- Strain:
- Wistar
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Age at study initiation: 8-10 weeks.
- Diet (e.g. ad libitum): standard pelleted diet, ad libitum.
- Water (e.g. ad libitum): tap water, ad libitum. - Route of administration:
- oral: drinking water
- Vehicle:
- water
- Details on exposure:
- VEHICLE
- Concentration in vehicle: 1 or 5 g Br-/l. - Analytical verification of doses or concentrations:
- not specified
- Details on mating procedure:
- 30 female rats were mated with 30 males of proven fertility.
- Duration of treatment / exposure:
- Days 2 to 28 postpartum.
- Frequency of treatment:
- Daily.
- Remarks:
- Doses / Concentrations:
0, 1 and 5 g Br-/l.
Basis:
nominal in water
(A dose of 5 g Br-/l water equals to a mean daily dose of bromide of about 220 mg). - No. of animals per sex per dose:
- 5 dams/group.
8 pups/dam. - Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: the bromide levels tested were chosen in compliance with the literature data, with the aim of ensuring that the mean intake of bromide in the animals would be effective and at the same time nonlethal.
- Maternal examinations:
- DETAILED CLINICAL OBSERVATIONS: Yes.
BODY WEIGHT: Yes
- Time schedule for examinations: at regular intervals.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study): Yes.
- Time schedule for examinations: at regular intervals.
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): Yes.
- Time schedule for examinations: at regular intervals. - Ovaries and uterine content:
- The ovaries and uterine content was examined after termination: No.
- Fetal examinations:
- - External examinations: Yes: size and weight were examined for each pup.
- Statistics:
- All statistical evaluation of the data was performed by nonparametric Kruskal-Wallis analysis of variance followed by the Mann-Whitney test for pairwise post hoc comparison. The difference is considered significant when p < 0.05.
- Details on maternal toxic effects:
- Maternal toxic effects:yes
Details on maternal toxic effects:
Food and water consumption: There was a gradual increase in the consumption of food in the course of lactation in both the control dams and the rats of the low-Br group, and there were no significant differences between these two groups with regard to the amount of food consumed. In the case of animals of the high-Br group, there were no changes in the food consumption during the whole lactation period. Starting from the second week of the nursing period, the amount of food consumed by these rats was markedly lower than that consumed by the control rats and the rat of the low-Br group. The same was true for the consumption of drinking water.
Body weight: the enhanced intake of bromide in the course of the lactation period did not influence significantly the body weight of the lactating rats of the low-Br group. In contrast, in the rats of the high-Br group, it caused a mild but gradual decrease of the average body weight. - Dose descriptor:
- LOAEL
- Effect level:
- 847.13 mg/kg bw/day (nominal)
- Based on:
- other: bromide ions.
- Basis for effect level:
- other: maternal toxicity
- Details on embryotoxic / teratogenic effects:
- Embryotoxic / teratogenic effects:yes
Details on embryotoxic / teratogenic effects:
Mortality: all of the pups in the control group survived, whereas in the low-Br and in the high-Br experimental groups, 94.8% and 56.3% of the young survived, respectively.
Body weight: there was a very marked effect of excess bromide on the body weight of the young whose mothers drank water with the addition of 5 g bromide per liter. The body weight in these suckling were progressively lower in comparison with the control young and the young of the low-Br group. - Dose descriptor:
- LOAEL
- Effect level:
- 847.13 mg/kg bw/day (nominal)
- Based on:
- other: bromide ions.
- Basis for effect level:
- other: teratogenicity
- Abnormalities:
- not specified
- Developmental effects observed:
- not specified
- Conclusions:
- The LOAEL for maternal toxicity and teratogenicity was established to be 847.13 mg Br-/kg bw/day (equivalent to 1086.88 mg NaBr/kg bw/day).
- Executive summary:
In the present study Female Wistar rats were mated and dosed with a high and a low dose of sodium bromide (5 and 1 g Br-/l, respectively) in their drinking water from 2nd to 28th day postpartum. Maternal examinations included clinical and body weight observations, as well as food and water consumption determinations. External examinations were performed for each pup. From the present study it can be concluded that excessive bromide intake in lactating rat dams affects both their own organisms and the organisms of their suckling young. However, marked effects were found only in dams that drank water with the addition of 5 bromide per liter (equivalent to a daily dose of bromide of about 220 mg per rat). In these dams a stagnation in the extent of the consumption of diet and water in the course of the nursing period were observed. Besides, as a consequence of an excessive intake of bromide in the course of the lactation period in the dams of the high-Br group, a gradual decrease in their average body weight was observed. Very pronounced effects of high bromide levels in the organism of the mothers were also observed in the young of the high-Br group. In this group, only 56% of the young survived. Their mean body weight on day 27 of life was less than 40% of the body weight of the control young and the general condition was very poor. Thus, the LOAEC for maternal toxicity and teratogenicity was established to be 220 mg bromide/day/rat (equivalent to 847.13 mg Br-/kg bw/day and 1086.88 mg NaBr/kg bw/day).
Reference
Table 1. Body Weight of the Dams on the 2nd, 15th, and 28th Postpartum Days, and the Difference Between the Values of the Body Weights at the End (28th day) and in the Beginning (2nd day) of the Nursing Period (Body Weight Gain).
Group |
Body weight (g) on post-partum day* |
|||
2 |
15 |
28 |
Difference (28-2) |
|
Control |
278.0 ± 16.9 |
302.8 ± 19.1 |
279.8 ± 20.5 |
1.8 ± 7.9 |
Low-Br |
248.0 ± 11.1 |
278.6 ± 8.0 |
262.6 ± 7.9 |
14.6 ± 11.2 |
High-Br |
286.2 ± 17.9 |
264.0 ± 40.2 |
229.0 ± 74.9 |
-57.2 ± 67.7a,b |
* Values are means ± SD, n = 5
a,bSignificantly diferent from the control group (ap = 0.008) and from the low-Br group (bp = 0.008).
Effect level: 5 g Bromide ions per liter was the lowest dose that produced adverse effects to the rats in the experiment. According to the author, this dose equals to a daily dose of bromide of about 220 mg per rat). Assuming a median weight of 259.7 g of the animals in the high bromide dose group, the lowest observed adverse effect level was established to be 847.13 mg Br-/kg bw/day, which equals to 1086.88 mg NaBr/kg bw/day.
Effect on developmental toxicity: via oral route
- Endpoint conclusion:
- adverse effect observed
- Dose descriptor:
- LOAEL
- 1 086.88 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
- Quality of whole database:
- Key study with Klimish = 2: Study well documented, meets generally accepted scientific principles, acceptable for assessment.
Effect on developmental toxicity: via inhalation route
- Endpoint conclusion:
- no study available
Effect on developmental toxicity: via dermal route
- Endpoint conclusion:
- no study available
Additional information
Key study: In the present study Female Wistar rats were mated and dosed with a high and a low dose of sodium bromide (5 and 1 g Br-/l, respectively) in their drinking water from 2nd to 28th day postpartum. Maternal examinations included clinical and body weight observations, as well as food and water consumption determinations. External examinations were performed for each pup. From the present study it can be concluded that excessive bromide intake in lactating rat dams affects both their own organisms and the organisms of their suckling young. However, marked effects were found only in dams that drank water with the addition of 5 bromide per liter (equivalent to a daily dose of bromide of about 220 mg per rat). In these dams a stagnation in the extent of the consumption of diet and water in the course of the nursing period were observed. Besides, as a consequence of an excessive intake of bromide in the course of the lactation period in the dams of the high-Br group, a gradual decrease in their average body weight was observed. Very pronounced effects of high bromide levels in the organism of the mothers were also observed in the young of the high-Br group. In this group, only 56% of the young survived. Their mean body weight on day 27 of life was less than 40% of the body weight of the control young and the general condition was very poor. Thus, the LOAEC for maternal toxicity and teratogenicity was established to be 220 mg bromide/day/rat (equivalent to 847.13 mg Br-/kg bw/day and 1086.88 mg NaBr/kg bw/day).
Justification for selection of Effect on developmental toxicity: via oral route:
Only one developmental toxicity study is available.
Justification for classification or non-classification
Based on the available information on toxicity to reproduction and developmental toxicity, sodium bromide is not classified for toxicity to reproduction in accordance with CLP Regulation (EC) No 1272/2008.
Additional information
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