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EC number: 237-401-7 | CAS number: 13772-29-7
- 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 bacteria
- Remarks:
- Type of genotoxicity: gene mutation
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2014-04-24 to 2014-05-13
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: well documented, according to OECD guideline and GLP
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 014
- Report date:
- 2014
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- Version / remarks:
- 1997
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.13/14 (Mutagenicity - Reverse Mutation Test Using Bacteria)
- Version / remarks:
- 2008
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 870.5100 - Bacterial Reverse Mutation Test (August 1998)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- Zirconium bis(hydrogen phosphate)
- EC Number:
- 237-401-7
- EC Name:
- Zirconium bis(hydrogen phosphate)
- Cas Number:
- 13772-29-7
- Molecular formula:
- H3O4P.1/2Zr
- IUPAC Name:
- hydrogen phosphate;zirconium(4+)
Constituent 1
Method
- Target gene:
- his trp
Species / strain
- Species / strain / cell type:
- S. typhimurium TA 1535, TA 1537, TA 98, TA 100 and E. coli WP2
- Metabolic activation:
- with and without
- Metabolic activation system:
- Phenobarbital/β-naphthoflavone induced rat liver S9
- Test concentrations with justification for top dose:
- Pre-experiment/Experiment I: 3; 10; 33; 100; 333; 1000; 2500; and 5000 µg/plate
Experiment II: 10; 33; 100; 333; 1000; 2500; and 5000 µg/plate - Vehicle / solvent:
- - Vehicle/solvent used: water
- Justification for choice of solvent/vehicle: The solvent was chosen because of its solubility properties and its relative nontoxicity to the bacteria.
Controls
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- sodium azide
- methylmethanesulfonate
- other: 4-nitro-o-phenylene-diamine, 2-aminoanthracene
- Remarks:
- With metabolic activation: 2-aminoanthracene (all strains), Without metabolic activation: sodium azide (TA 1535), 2-aminoanthracene , 4-nitro-o-phenylene-diamine(TA 1537, TA 98), methyl methane sulfonate (E. coli)
- Details on test system and experimental conditions:
- DETAILS ON TEST SYSTEM
METHOD OF APPLICATION: in agar (plate incorporation); preincubation
DURATION
- Preincubation period: 20 min
- Exposure duration: 37°C for 48 - 72 hours
NUMBER OF REPLICATIONS: 3
DETERMINATION OF CYTOTOXICITY
Toxicity detected by a
- decrease in the number of revertants
- clearing or diminution of the background lawn (= reduced his- or trp- background growth)
- reduction in the titer - Evaluation criteria:
- A test item is considered as a mutagen if a biologically relevant increase in the number of revertants exceeding the threshold of twice (strains TA 98, TA 100, and WP2 uvrA) or thrice (strains TA 1535 and TA 1537) the colony count of the corresponding solvent control is observed.
A dose dependent increase is considered biologically relevant if the threshold is exceeded at more than one concentration.
An increase exceeding the threshold at only one concentration is judged as biologically relevant if reproduced in an independent second experiment.
A dose dependent increase in the number of revertant colonies below the threshold is regarded as an indication of a mutagenic potential if reproduced in an independent second experiment. However, whenever the colony counts remain within the historical range of negative and solvent controls such an increase is not considered biologically relevant. - Statistics:
- According to the OECD guideline 471, a statistical analysis of the data is not mandatory.
Results and discussion
Test results
- Species / strain:
- S. typhimurium TA 1535, TA 1537, TA 98, TA 100 and E. coli WP2
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity nor precipitates, but tested up to recommended limit concentrations
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- Precipitation of the test item in the overlay agar on the incubated agar plates was observed from 1000 to 5000 µg/plate in both experiments with and without S9 mix. The undissolved particles had no influence on the data recording.
No toxic effects, evident as a reduction in the number of revertants (below the indication factor of 0.5), occurred in the test groups with and without metabolic activation in both experiments - Remarks on result:
- other: all strains/cell types tested
- Remarks:
- Migrated from field 'Test system'.
Any other information on results incl. tables
Table 1: Number of revertants per plate (mean of three plates), Experiment 1
strain TA 1535 |
strain TA 1537 |
Strain TA 98 |
strain TA 100 |
E. coli WP2 uvrA |
||||||
conc. [µg] |
-MA |
+MA |
-MA |
+MA |
-MA |
+MA |
-MA |
+MA |
-MA |
+MA |
deionized water |
20 |
16 |
8 |
21 |
29 |
46 |
184 |
193 |
46 |
50 |
0 |
12 |
16 |
7 |
17 |
27 |
49 |
178 |
195 |
36 |
47 |
3 |
19 |
17 |
11 |
21 |
27 |
48 |
200 |
189 |
39 |
44 |
10 |
17 |
17 |
10 |
21 |
32 |
45 |
193 |
199 |
42 |
47 |
33 |
16 |
18 |
10 |
19 |
32 |
50 |
204 |
210 |
40 |
52 |
100 |
18 |
16 |
7 |
17 |
26 |
42 |
190 |
205 |
39 |
48 |
333 |
16 |
20 |
9 |
21 |
27 |
41 |
194 |
203 |
41 |
46 |
1000 |
15 |
14* |
9* |
24* |
30* |
46* |
216* |
197* |
48* |
38* |
2500 |
15 |
18* |
6* |
22* |
25* |
39* |
199* |
196* |
39* |
46* |
5000 |
11 |
12* |
7* |
11* |
24* |
37* |
190* |
209* |
47* |
56* |
Sodium azide 10 µg |
3339 |
|
|
|
|
|
1871 |
|
|
|
4-nitro-o-phenylene-diamine 10 µg |
|
|
|
|
294 |
|
|
|
|
|
4-nitro-o-phenylene-diamine 50 µg |
|
|
62 |
|
|
|
|
|
|
|
methyl methane sulfonate 2 µL |
|
|
|
|
|
|
|
|
822 |
|
2-aminoanthracene 2.5 µg |
|
619 |
|
371 |
|
3510 |
|
3403 |
|
|
2-aminoanthracene 10 µg |
|
|
|
|
|
|
|
|
|
470 |
*Precipitate
Table 2: Number of revertants per plate (mean of three plates), Experiment 2
strain TA 1535 |
strain TA 1537 |
Strain TA 98 |
strain TA 100 |
E. coli WP2 uvrA |
||||||
conc. [µg] |
-MA |
+MA |
-MA |
+MA |
-MA |
+MA |
-MA |
+MA |
-MA |
+MA |
deionized water |
17 |
24 |
10 |
18 |
29 |
44 |
176 |
199 |
40 |
53 |
0 |
12 |
18 |
11 |
17 |
25 |
33 |
193 |
206 |
44 |
41 |
10 |
14 |
22 |
10 |
22 |
27 |
41 |
205 |
217 |
39 |
47 |
33 |
19 |
21 |
9 |
19 |
27 |
41 |
209 |
205 |
35 |
52 |
100 |
19 |
24 |
9 |
9 |
29 |
46 |
180 |
232 |
40 |
55 |
333 |
15 |
19 |
9 |
21 |
27 |
42 |
199 |
198 |
43 |
43 |
1000 |
21* |
15* |
10* |
15* |
29* |
40* |
204* |
215* |
42* |
53* |
2500 |
8* |
13* |
8* |
17* |
29* |
50* |
189* |
200* |
44* |
49* |
5000 |
11* |
13* |
8* |
14* |
22* |
34* |
178* |
210* |
35* |
53* |
Sodium azide 10 µg |
3206 |
|
|
|
|
|
1667 |
|
|
|
4-nitro-o-phenylene-diamine 10 µg |
|
|
|
|
274 |
|
|
|
|
|
4-nitro-o-phenylene-diamine 50 µg |
|
|
63 |
|
|
|
|
|
|
|
methyl methane sulfonate 2 µL |
|
|
|
|
|
|
|
|
461 |
|
2-aminoanthracene 2.5 µg |
|
531 |
|
316 |
|
3348 |
|
2735 |
|
|
2-aminoanthracene 10 µg |
|
|
|
|
|
|
|
|
|
264 |
*Precipitate
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information):
negative
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