Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
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

Genetic toxicity: in vitro
Administrative data
- Endpoint:
- in vitro gene mutation study in mammalian cells
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- 1997-08-05 to 1997-10-13
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP Guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 198
- Report date:
- 1998
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 476 (In Vitro Mammalian Cell Gene Mutation Test)
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.5300 - In vitro Mammalian Cell Gene Mutation Test
- GLP compliance:
- yes
- Type of assay:
- mammalian cell gene mutation assay
Test material
- Reference substance name:
- Ammonium bromide
- EC Number:
- 235-183-8
- EC Name:
- Ammonium bromide
- Cas Number:
- 12124-97-9
- Molecular formula:
- BrH4N
- IUPAC Name:
- ammonium bromide
- Details on test material:
- - Name of test material (as cited in study report): Ammonium bromide
- Physical state: White powder
- Analytical purity: 98.5%
- Lot/batch No.: 970027/1
Sodium bromide is an inorganic salt that dissociates to its composite ions in aqueous solutions at environmental pH and temperature. Comparison of the available data on the various bromide salts have shown that the bromide ion is the relevant ion for determination of the toxicological profile with simple cations such as potassium, sodium or ammonium, that are ubiquitous in nature, having little or no influence on the bromide ion properties. It is therefore justified to read-across data from other inorganic bromide salts to sodium bromide.
Constituent 1
Method
- Target gene:
- Mouse lymphoma L5178Y cells (clone 3.7.2.C)
Species / strain
- Species / strain / cell type:
- mouse lymphoma L5178Y cells
- Metabolic activation:
- with and without
- Metabolic activation system:
- Arochlor induced rat liver S9
- Test concentrations with justification for top dose:
- Toxicity Test:
0.5/1.5/5/15/150/500/1500/5000 µg/mL
Mutagenicity Assays:
(1000)/2000/3000/4000/5000 µg/mL both in presence and absence of S9 mix - Vehicle / solvent:
- - Vehicle(s)/solvent(s) used: water
- Justification for choice of solvent/vehicle: solubility
Controls
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- no
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: Ethylmethanesulphonate (dissolved in dimethylsulphoxide) and Methylmethanesulphonate (dissolved in water) in the absence of S9 mix; 3-methylcholanthrene (dissolved in dimethylsulphoxide) in presence of S9 mix
- Details on test system and experimental conditions:
- The test substance was dissolved in water and cells exposed to 1000-5000 µg/mL final concentration both in the presence and absence of metabolic activation (S9 mix). Cell sample cultures were incubated either with test solution, vehicle or positive control for four hours at 37°C and 10 rpm on a rotating drum. After this, cells were sedimented (200 g, 5 min) and resuspended in fresh medium (20 mL). To reach a cell density of 3 x 105/mL this step was repeated. Cells were returned to the rotating drum and allowed for expression of genetic lesions for 2 days at 37°C. On Day 2 all control cultures plus the cultures from the 4 highest concentrations giving adequate survival were selected for expression of genetic damage. This was determined by performing 2 parallel cloning assays: the viability assay and the mutant selection assay. For the viability assay each culture was diluted (2 x 103 cells/ml) and three samples of 0,1 ml were added to 25 ml of cloning medium, poured into a 90 mm Petri dish, giving 200 cells per plate. For the mutant selection assay, trifluorothymidine (TFT) stock solution was added to the cloning medium to a final concentration of 3µg/ml. Duplicate samples of cells (1,5 x 106) were suspended in 2 x 25 ml cloning medium (containing TFT) and poured into Petri dishes (100 mm). The dishes were prepoured with cloning medium to make an underlay (20 ml each). This underlay compensates for the larger volume of Petri dishes and prevents the cells from making contact with the floor of the dish. All plates were gelled at room temperature until the agar had set, then incubated at 37°C in an atmosphere of 5% Co2:95% air until the colonies were fully developed (usually 14 days). The colonies were then counted using a “Domino” image analyser.
Doses in mutation experiments should extend into the toxic range, the maximum usable limit allowing cell growth and subsequent cloning efficiency giving at least 10% of the concurrent vehicle control values. Therefore a initial toxicity test was performed in the absence and presence of S9 mix. Concentrations of ammonium bromide used were in the range of 0,5 – 5000 µg/ml. Exposure of cells was similar to that of the mutation assays. Following treatment the cell population densities were recorded over two days using a haemocytometer, then the total suspension growths were expressed as percentages of the vehicle control group. - Evaluation criteria:
- Results from any tube of exposed cells were rejected if mean cloning efficency was greater than 120%.
Results from any treatment were inadequate if there were less than 2 acceptable cultures. Where results were obtained from a single culture, they may have been included as supporting evidence.
Controls
Results from the vehicle cultures were rejected if mean cloning efficency was less than 60%.
Results from vehicle control cultures were required to give a mean mutant fraction less than 150 per 10E06 survivors and at least 20 per 10E06 survivors.
Results from positive control cultures were required to give mutant fractions of at least double the vehicle control value and equal to or greater than 100 per 10E06 survivors. Cloning efficiencies greater than 10% were also required.
Test materials
Individal cultures were rejected if the relative growth was less than 10% of the mean vehicle control or cloning efficiency after the expression period was less than 10%.
An experiment was liable to rejection of there were acceptable results from less than 3 dose levels.
Interpretation of toxicity
Results should be obtained from concentrations in RTG range 10- 20%
Test negative if test material response not significantly higher than negative control at pre-set limit (reduction of total relative growth to 20% or 5000 µg/mL)
Positive response: response at a single dose is significant if cloning efficiency is at least 10% of concurrent vehicle and mean mutant fraction of 2 cultures is at least 1.7 fold higher than the mean control value.
Test material positive if 2/2 positive experiments recorded with same activation condition or if in one or other activation condition; the first experiment indicated a positive but did not meet the criteria due to lack of results from a critically toxic concentration; the second experiment gave an unequivocal positive. - Statistics:
- Weak positive and equivocal results can be subjected to statistical analysis by ANOVA and t-test, for confirmation of the significance of the response.
Results and discussion
Test results
- Species / strain:
- mouse lymphoma L5178Y cells
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- cytotoxicity
- Remarks:
- 5000 µg/mL
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- -S9: No evidence of mutagenic activity was obtained in any ammonium bromide-treated cultures. The mean relative total growth at the highest concentration (5000 µg/ml) were 57,5% and 73,5% in the absence of S9 mix. These experiment was classed as negative.
+S9: No evidence of mutagenic activity was obtained in any ammonium bromide-treated cultures. The mean relative total growth at the highest concentration (5000 µg/ml) were 58% and 71% in the presence of S9 mix. These experiment was classed as negative.
Cytotoxicity: At a concentration of 5000 µg/mL ammonium bromide caused significant reduction in relative suspension growth both in the presence and in the absence of S9 mix. - Remarks on result:
- other: all strains/cell types tested
- Remarks:
- Migrated from field 'Test system'.
Any other information on results incl. tables
Table 1: Results of Mouse Lymphoma Mutation Test absence and presence of metabolic activation (S9 mix)
Chemical |
Concentration [µg/ml] |
Without S9 mix |
With S9 mix |
||||||
assay 1 |
assay 3 |
assay 2 |
assay 4 |
||||||
Mutant fraction* |
RTG % |
Mutant fraction* |
RTG % |
Mutant fraction* |
RTG % |
Mutant fraction* |
RTG % |
||
Water |
(100 µl added) |
24 |
87 |
35 |
93 |
26 |
109 |
38 |
98 |
47 |
82 |
39 |
87 |
32 |
103 |
38 |
100 |
||
19 |
119 |
49 |
106 |
20 |
97 |
37 |
87 |
||
33 |
112 |
52 |
114 |
36 |
91 |
37 |
116 |
||
EMS |
250 |
235 |
38 |
332 |
68 |
- |
- |
- |
- |
244 |
41 |
301 |
79 |
- |
- |
- |
- |
||
MMS |
15 |
266 |
19 |
206 |
16 |
- |
- |
- |
- |
294 |
16 |
267 |
18 |
- |
- |
- |
- |
||
3-MC |
2,5 |
- |
- |
- |
- |
200 |
32 |
250 |
61 |
- |
- |
- |
- |
199 |
29 |
244 |
54 |
||
Ammonium Bromide |
2000 |
30 |
103 |
47 |
84 |
28 |
100 |
36 |
93 |
25 |
67 |
44 |
87 |
25 |
95 |
34 |
87 |
||
3000 |
45 |
63 |
34 |
83 |
19 |
86 |
32 |
87 |
|
30 |
80 |
32 |
80 |
26 |
86 |
42 |
83 |
||
4000 |
20 |
70 |
45 |
62 |
29 |
68 |
39 |
60 |
|
28 |
70 |
43 |
54 |
19 |
71 |
39 |
64 |
||
5000 |
17 |
59 |
34 |
68 |
15 |
62 |
33 |
72 |
|
24 |
56 |
45 |
79 |
29 |
54 |
35 |
70 |
EMS Ethylmethanesulphonate
MMS Methylmethanesulphonate
3-MC 3-methylcholanthrene
* [x 106] 200 (total mutant count) / (total viable count)
RTG relative total growth
Table 2: Results of Mouse Lymphoma Toxicity Test (Pre-Test) in the absence and presence of metabolic activation (S9 mix)
Chemical |
Concentration (µg/ml) |
Without S9 mix |
With S9 mix |
||||||
Daily Suspension Count x 105/ml |
Total Suspension Growth |
RSG % |
Daily Suspension Count x 105/ml |
Total Suspension Growth |
RSG % |
||||
Day 1 |
Day 2 |
Day 1 |
Day 2 |
||||||
Water |
100 µl added |
11.4 |
15.2 |
19.3 |
100 |
11 |
15.2 |
18.6 |
100 |
Ammonium Bromide |
0,5 |
12.6 |
15.2 |
21.3 |
110 |
11.6 |
15 |
19.3 |
104 |
1,5 |
11.4 |
14 |
17.7 |
92 |
12 |
14.2 |
18.9 |
102 |
|
5 |
14 |
14.6 |
22.7 |
118 |
11.2 |
16.6 |
20.7 |
111 |
|
15 |
13.6 |
13.4 |
20.2 |
105 |
13.2 |
11 |
16.1 |
87 |
|
50 |
15 |
13.8 |
23 |
119 |
11.2 |
11 |
13.7 |
74 |
|
150 |
12.4 |
15.2 |
20.9 |
108 |
11.6 |
11.2 |
14.4 |
77 |
|
500 |
14.8 |
12.4 |
20.4 |
106 |
11.2 |
11 |
13.7 |
74 |
|
1500 |
14.4 |
13.6 |
21.8 |
113 |
10.4 |
12.6 |
14.6 |
78 |
|
5000 |
7 |
14 |
10.9 |
56 |
4.7 |
12.6 |
6.6 |
35 |
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information):
negative
Ammonium bromide is not mutagenic in mouse lymphoma L5178Y cells when tested to the pre-set maximum concentration of 5000 µg/ml both in the presence and absence of a metabolic activation system - Executive summary:
The objective of the study was to determine the potential of ammonium bromide to induce mutations at the thymidine kinase locus: tk+tk-to tk-tk-of mouse lymphoma L5178Y cells.
The test substance was dissolved in water and cells exposed to 1000-5000 µg/mL final concentration both in the presence and absence of metabolic activation (S9 mix). Cell sample cultures were incubated either with test solution, vehicle or positive control for four hours at 37°C and 10 rpm on a rotating drum. After this, cells were sedimented (200 g, 5 min) and resuspended in fresh medium (20 mL). To reach a cell density of 3 x 105/mL this step was repeated. Cells were returned to the rotating drum and allowed for expression of genetic lesions for 2 days at 37°C. On Day 2 all control cultures plus the cultures from the 4 highest concentrations giving adequate survival were selected for expression of genetic damage. This was determined by performing 2 parallel cloning assays: the viability assay and the mutant selection assay. For the viability assay each culture was diluted (2 x 103cells/ml) and three samples of 0,1 ml were added to 25 ml of cloning medium, poured into a 90 mm Petri dish, giving 200 cells per plate. For the mutant selection assay, trifluorothymidine (TFT) stock solution was added to the cloning medium to a final concentration of 3µg/ml. Duplicate samples of cells (1,5 x 106) were suspended in 2 x 25 ml cloning medium (containing TFT) and poured into Petri dishes (100 mm). The dishes were prepoured with cloning medium to make an underlay (20 ml each). This underlay compensates for the larger volume of Petri dishes and prevents the cells from making contact with the floor of the dish. All plates were gelled at room temperature until the agar had set, then incubated at 37°C in an atmosphere of 5% Co2:95% air until the colonies were fully developed (usually 14 days). The colonies were then counted using a “Domino” image analyser.
Doses in mutation experiments should extend into the toxic range, the maximum usable limit allowing cell growth and subsequent cloning efficiency giving at least 10% of the concurrent vehicle control values. Therefore a initial toxicity test was performed in the absence and presence of S9 mix. Concentrations of ammonium bromide used were in the range of 0,5 – 5000 µg/ml. Exposure of cells was similar to that of the mutation assays. Following treatment the cell population densities were recorded over two days using a haemocytometer, then the total suspension growths were expressed as percentages of the vehicle control group.
The preliminary toxicity test showed that ammonium bromide caused a significant reduction in the relative suspension growth only at the pre-set maximum concentration of 5000 µg/ml (56 % and 35 % in the absence and presence of s9 mix respectively).
No evidence of mutagenic activity was obtained from cultures treated with ammonium bromide in any of the 4 assays with and without metabolic activation. The solvent control values were within the normal ranges experienced in the performing laboratory and reported in the literature with the L5178Y cell line. The high mutant fractions obtained with EMS, MMS and 3-MC were within the normal ranges. 3-MC (which is not mutagenic in the absence of S9 mix) proved the efficacy of the S9.
Ammonium bromide is not mutagenic in mouse lymphoma L5178Y cells when tested to the pre-set maximum concentration of 5000 µg/ml both in the presence and absence of a metabolic activation system.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
