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EC number: 236-875-2 | CAS number: 13530-50-2
- 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
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Between 22 December 2009 and 05 February 2010
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
See read-across justification report under Section 13 ‘Assessment Reports’.
1. HYPOTHESIS FOR THE ANALOGUE APPROACH
In accordance with REACH Annex XI, Section 1.5, of Regulation (EC) No. 1907/2006 (REACH) the standard testing regime may be adapted in cases where a grouping or read-across approach has been applied.
The similarities may be based on:
(1) a common functional group
(2) the common precursors and/or the likelihood of common breakdown products via physical or biological processes, which result in structurally similar chemicals; or
(3) a constant pattern in the changing of the potency of the properties across the category
The source substance and the target substance are considered to be similar enough to facilitate read-across for the following reasons:
(1) Both substances are inorganic salts containing a trivalent aluminium cation and phosphoric acid. Thus, they all share the Al3+ cation and the PO43- anion as common functional groups. The source substance also contains an Na+ ion, this is not expected to influence the toxicological profile of the substance. Therefore the toxicity of the above substances will be predominantly determined by the presence of the Al3+ cation.
(2) Both substances will ultimately dissociate into the common breakdown products of the Al3+ cations and the PO43- anion.
(3) In general, independently of the cation under consideration, the water solubility of phosphates decreases with increasing degree of phosphate condensation (orthophosphate > diphosphate > triphosphate > polyphosphate).
In accordance with the provisions set out in Annex XI, Section 1.5, the results of the studies used for assessment and read-across are adequate for the purpose of classification and labelling and/or risk assessment; have adequate and reliable coverage of the key parameters addressed in the corresponding test method; cover an exposure duration comparable to or longer than the corresponding test method; and adequate and reliable documentation of the applied method is provided in the technical dossier. Orthophosphates are not considered to be genotoxic and are essential micronutrients. As such the genotoxicity potential of the target substance will be predominantly determined by the presence of the Al3+ cation. On this basis the standard testing requirements, as detailed in Regulation (EC) 1907/2006 (REACH) were conducted on aluminium orthophosphate as this substance contains the greatest amount of aluminium (%w/w) in comparison to the target substance. This approach is considered to be reliable and justified and no further testing for aluminium tris(dihydrogenorthophosphate) is required.
2. SOURCE AND TARGET CHEMICAL(S) (INCLUDING INFORMATION ON PURITY AND IMPURITIES)
See read-across justification report under Section 13 ‘Assessment Reports’.
3. ANALOGUE APPROACH JUSTIFICATION
See read-across justification report under Section 13 ‘Assessment Reports’.
4. DATA MATRIX
See read-across justification report under Section 13 ‘Assessment Reports’.
Cross-reference
- Reason / purpose for cross-reference:
- assessment report
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method B.13/14 (Mutagenicity - Reverse Mutation Test Using Bacteria)
- Deviations:
- no
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- EPA OPPTS 870.5100 - Bacterial Reverse Mutation Test (August 1998)
- Deviations:
- no
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- JAPAN: Guidelines for Screening Mutagenicity Testing Of Chemicals
- Deviations:
- no
- Principles of method if other than guideline:
- Not applicable.
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Date of GLP inspection: 15 September 2009 Date of Signature on GLP certificate: 26 November 2009
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- Aluminium orthophosphate (M 13-03)
- IUPAC Name:
- Aluminium orthophosphate (M 13-03)
- Reference substance name:
- 22784-12-9
- EC Number:
- 607-158-5
- Cas Number:
- 22784-12-9
- IUPAC Name:
- 22784-12-9
- Reference substance name:
- Aluminium orthophosphate
- EC Number:
- 232-056-9
- EC Name:
- Aluminium orthophosphate
- Cas Number:
- 7784-30-7
- Molecular formula:
- Al.H3O4P
- IUPAC Name:
- [phosphato(3-)-kappa~3~O,O',O'']aluminum
Constituent 1
Constituent 2
Constituent 3
Method
- Target gene:
- Histidine for Salmonella.
Tryptophan for E.Coli
Species / strainopen allclose all
- Species / strain / cell type:
- S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
- Details on mammalian cell type (if applicable):
- Not applicable.
- Additional strain / cell type characteristics:
- not applicable
- Species / strain / cell type:
- E. coli WP2 uvr A
- Details on mammalian cell type (if applicable):
- Not applicable.
- Additional strain / cell type characteristics:
- not applicable
- Metabolic activation:
- with and without
- Metabolic activation system:
- phenobarbitone/betanaphthoflavone induced rat liver, S9
- Test concentrations with justification for top dose:
- Preliminary Toxicity Test: 0, 0.15, 0.5, 1.5, 5, 15, 50, 150, 500, 1500 and 5000 µg/plate
main test:
Experiment one: 50, 150, 500, 1500 and 5000 µg/plate
Experiment two: 50, 150, 500, 1500 and 5000 µg/plate - Vehicle / solvent:
- EXAMPLE
- Vehicle(s)/solvent(s) used: dimethyl sulphoxide
- Justification for choice of solvent/vehicle: The test material was insoluble in sterile distilled water, dimethyl sulphoxide, acetone, dimethyl formamide and acetonitrile at 50 mg/ml and tetrahydrofuran at 200 mg/ml in solubility checks performed in–house. The test material formed the best doseable suspension in dimethyl sulphoxide, therefore, this solvent was selected as the vehicle.
Controlsopen allclose all
- Untreated negative controls:
- yes
- Remarks:
- Spontaneous mutation rate for TA100
- Negative solvent / vehicle controls:
- yes
- Remarks:
- DMSO
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- N-ethyl-N-nitro-N-nitrosoguanidine
- Remarks:
- Without S9 mix Migrated to IUCLID6: at 3 µg/plate
- Untreated negative controls:
- yes
- Remarks:
- Spontaneous mutation rate for TA100
- Negative solvent / vehicle controls:
- yes
- Remarks:
- DMSO
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: 2-Aminoanthracene at 1 µg/plate
- Remarks:
- With S9 mix
- Untreated negative controls:
- yes
- Remarks:
- Spontaneous mutation rate for TA1535
- Negative solvent / vehicle controls:
- yes
- Remarks:
- DMSO
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- N-ethyl-N-nitro-N-nitrosoguanidine
- Remarks:
- without S9 mix Migrated to IUCLID6: at 5µg/plate
- Untreated negative controls:
- yes
- Remarks:
- Spontaneous mutation rate for TA1535
- Negative solvent / vehicle controls:
- yes
- Remarks:
- DMSO
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- 9-aminoacridine
- Remarks:
- with S9 mix Migrated to IUCLID6: 2-Aminoanthracene at 2 µg/plate
- Untreated negative controls:
- yes
- Remarks:
- Spontaneous mutation rate for WP2uvrA
- Negative solvent / vehicle controls:
- yes
- Remarks:
- DMSO
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- N-ethyl-N-nitro-N-nitrosoguanidine
- Remarks:
- without S9 mix Migrated to IUCLID6: at 2 µg/plate
- Untreated negative controls:
- yes
- Remarks:
- Spontaneous mutation rate for WP2uvrA
- Negative solvent / vehicle controls:
- yes
- Remarks:
- DMSO
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: 2-Aminoanthracene at 10 µg/plate
- Untreated negative controls:
- yes
- Remarks:
- Spontaneous mutation rate for TA98
- Negative solvent / vehicle controls:
- yes
- Remarks:
- DMSO
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- 4-nitroquinoline-N-oxide
- Remarks:
- without S9 mix Migrated to IUCLID6: at 0.2 µg/plate
- Untreated negative controls:
- yes
- Remarks:
- Spontaneous muation rate for TA98
- Negative solvent / vehicle controls:
- yes
- Remarks:
- DMSO
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- benzo(a)pyrene
- Remarks:
- with S9 mix Migrated to IUCLID6: at 5 µg/plate
- Untreated negative controls:
- yes
- Remarks:
- Spontaneous mutation rate for TA1537
- Negative solvent / vehicle controls:
- yes
- Remarks:
- DMSO
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- 9-aminoacridine
- Remarks:
- without S9 mix Migrated to IUCLID6: at 80 µg/plate
- Untreated negative controls:
- yes
- Remarks:
- Sponateous muation rate for TA1537
- Negative solvent / vehicle controls:
- yes
- Remarks:
- DMSO
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: 2-Aminoanthracene at 2 µg/plate
- Remarks:
- with S9 mix
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: in agar (plate incorporation)
DURATION
- Preincubation period: 10h
- Exposure duration: 48 - 72 hrs
- Expression time (cells in growth medium): Not applicable
- Selection time (if incubation with a selection agent): Not applicable
- Fixation time (start of exposure up to fixation or harvest of cells): 48 -72 hrs
SELECTION AGENT (mutation assays): Not applicable.
NUMBER OF REPLICATIONS: Triplicate plating.
NUMBER OF CELLS EVALUATED: Not applicable.
DETERMINATION OF CYTOTOXICITY
- Method: plates were assessed for numbers of revertant colonies and examined for effects on the growth of the bacterial background lawn.
OTHER EXAMINATIONS: None - Evaluation criteria:
- Acceptance Criteria:
The reverse mutation assay may be considered valid if the following criteria are met:
All tester strain cultures exhibit a characteristic number of spontaneous revertants per plate in the vehicle and untreated controls.
The appropriate characteristics for each tester strain have been confirmed, eg rfa cell-wall mutation and pKM101 plasmid R-factor etc.
All tester strain cultures should be in the approximate range of 1 to 9.9 x 10E9 bacteria per ml.
Each mean positive control value should be at least twice the respective vehicle control value for each strain, thus demonstrating both the intrinsic sensitivity of the tester strains to mutagenic exposure and the integrity of the S9-mix.
There should be a minimum of four non-toxic test material dose levels.
There should not be an excessive loss of plates due to contamination.
Evaluation criteria:
There are several criteria for determining a positive result, such as a dose-related increase in revertant frequency over the dose range tested and/or a reproducible increase at one or more concentrations in at least one bacterial strain with or without metabolic activation. Biological relevance of the results will be considered first, statistical methods, as recommended by the UKEMS can also be used as an aid to evaluation, however, statistical significance will not be the only determining factor for a positive response.
A test material will be considered non-mutagenic (negative) in the test system if the above criteria are not met.
Although most experiments will give clear positive or negative results, in some instances the data generated will prohibit a definitive judgement about the test material activity. Results of this type will be reported as equivocal. - Statistics:
- Standard deviation
Results and discussion
Test resultsopen allclose all
- Species / strain:
- E. coli WP2 uvr A
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity nor precipitates, but tested up to recommended limit concentrations
- Remarks:
- Tested up to maximum recommended dose of 5000 micro.g/plate
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Species / strain:
- S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity nor precipitates, but tested up to recommended limit concentrations
- Remarks:
- Tested up to maximum recommended dose of 5000 micro.g/plate
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- TEST-SPECIFIC CONFOUNDING FACTORS
- Water solubility: The test material formed the best doseable suspension in dimethyl sulphoxide at 50 mg/ml in solubility checks performed in-house.
- Precipitation: A pale, fine precipitate was observed at 5000 µg/plate, this observation did not prevent the scoring of revertant colonies.
RANGE-FINDING/SCREENING STUDIES:
Preliminary Toxicity Test:
The test material was non-toxic to the strains of bacteria used (TA100 and WP2uvrA-). The test material formulation and S9-mix used in this experiment were both shown to be sterile.
COMPARISON WITH HISTORICAL CONTROL DATA:
Prior to use, the master strains were checked for characteristics, viability and spontaneous reversion rate (all were found to be satisfactory).
Results for the negative controls (spontaneous mutation rates) were considered to be acceptable.
All of the positive control chemicals used in the test induced marked increases in the frequency of revertant colonies thus confirming the activity of the S9-mix and the sensitivity of the bacterial strains.
ADDITIONAL INFORMATION ON CYTOTOXICITY: None - Remarks on result:
- other: all strains/cell types tested
- Remarks:
- Migrated from field 'Test system'.
Any other information on results incl. tables
Preliminary Toxicity Test
The test material was non-toxic to the strains of bacteria used (TA100 and WP2uvrA-)
The numbers of revertant colonies for the toxicity assay were:
With (+) or without (-) S9-mix |
Strain |
Dose (µg/plate) |
||||||||||
0 |
0.15 |
0.5 |
1.5 |
5 |
15 |
50 |
150 |
500 |
1500 |
5000 |
||
- |
TA100 |
82 |
105 |
111 |
111 |
114 |
108 |
109 |
126 |
109 |
103 |
120P |
+ |
TA100 |
104 |
94 |
99 |
50 |
63 |
83 |
69 |
82 |
90 |
77 |
92P |
- |
WP2uvrA- |
26 |
26 |
20 |
29 |
26 |
32 |
15 |
25 |
19 |
29 |
28P |
+ |
WP2uvrA- |
28 |
32 |
30 |
25 |
31 |
26 |
29 |
27 |
28 |
24 |
25P |
P Precipitate
The test material caused a visible reduction in the growth of the bacterial background lawn of Salmonella strain TA100, without S9-mix, at 5000 µg/plate in the range-finding test only. However, this response was not observed in either the preliminary toxicity test or main test and was, therefore, considered spurious and of no biological relevance. No toxicity was noted to any of the remaining bacterial tester strains at any test material dose level in either the absence or presence of S9-mix. The test material was, therefore, tested up to the maximum recommended dose level of 5000 µg/plate. A pale, fine precipitate was observed at 5000 µg/plate, this observation did not prevent the scoring of revertant colonies.
No significant increases in the frequency of revertant colonies were recorded for any of the bacterial strains, at any dose level either with or without metabolic activation or exposure method.
All of the positive control chemicals used in the test induced marked increases in the frequency of revertant colonies thus confirming the activity of the S9-mix and the sensitivity of the bacterial strains.
The individual plate counts, the mean number of revertant colonies and the standard deviations for the test material, vehicle and positive controls both with and without metabolic activation for the Main test are presented in the tables below:
Spontaneous Mutation Rates (Concurrent Negative Controls)
Range-finding Test (Experiment 1)
Number of revertants (mean number of colonies per plate) |
|||||||||
Base-pair substitution type |
Frameshift type |
||||||||
TA100 |
TA1535 |
WP2uvrA- |
TA98 |
TA1537 |
|||||
93 |
|
14 |
|
43 |
|
13 |
|
11 |
|
120 |
(110) |
13 |
(16) |
24 |
(33) |
23 |
(19) |
11 |
(12) |
118 |
|
22 |
|
33 |
|
20 |
|
14 |
|
Main Test (Experiment 2)
Number of revertants (mean number of colonies per plate) |
|||||||||
Base-pair substitution type |
Frameshift type |
||||||||
TA100 |
TA1535 |
WP2uvrA- |
TA98 |
TA1537 |
|||||
100 |
|
20 |
|
21 |
|
22 |
|
5 |
|
102 |
(101) |
18 |
(19) |
16 |
(20) |
22 |
(22) |
7 |
(7) |
100 |
|
18 |
|
24 |
|
21 |
|
9 |
|
Test Results: Range-Finding Test– Without Metabolic Activation
Test Period |
From: 17 January 2010 |
To: 20 January 2010 |
||||||||||
With or without S9-Mix |
Test substance concentration (µg/plate) |
Number of revertants (mean number of colonies per plate) |
||||||||||
Base-pair substitution type |
Frameshift type |
|||||||||||
TA100 |
TA1535 |
WP2uvrA‑ |
TA98 |
TA1537 |
||||||||
- |
0 |
102 95 99 |
(99) 3.5# |
29 31 19 |
(26) 6.4 |
36 35 40 |
(37) 2.6 |
20 21 13 |
(18) 4.4 |
8 13 16 |
(12) 4.0 |
|
- |
50 |
97 72 91 |
(87) 13.1 |
26 28 24 |
(26) 2.0 |
35 36 37 |
(36) 1.0 |
21 16 15 |
(17) 3.2 |
19 19 11 |
(16) 4.6 |
|
- |
150 |
80 88 81 |
(83) 4.4 |
21 30 32 |
(28) 5.9 |
38 38 38 |
(38) 0.0 |
19 17 22 |
(19) 2.5 |
21 13 14 |
(16) 4.4 |
|
- |
500 |
87 85 91 |
(88) 3.1 |
20 24 16 |
(20) 4.0 |
33 36 41 |
(37) 4.0 |
15 14 10 |
(13) 2.6 |
11 16 14 |
(14) 2.5 |
|
- |
1500 |
91 94 90 |
(92) 2.1 |
24 21 16 |
(20) 4.0 |
37 36 41 |
(38) 2.6 |
22 11 20 |
(18) 5.9 |
11 15 13 |
(13) 2.0 |
|
- |
5000 |
62 TP 64 TP 83 TP |
(70) 11.6 |
21 P 30 P 12 P |
(21) 9.0 |
31 P 43 P 34 P |
(36) 6.2 |
18 P 21 P 28 P |
(22) 5.1 |
14 P 16 P 14 P |
(15) 1.2 |
|
Positive controls
S9-Mix
- |
Name Concentration (μg/plate) No. colonies per plate |
ENNG |
ENNG |
ENNG |
4NQO |
9AA |
||||||
3 |
5 |
2 |
0.2 |
80 |
||||||||
530 657 665 |
(617) 75.7 |
1521 1622 1317 |
(1487) 155.4 |
913 956 898 |
(922) 30.1 |
153 156 188 |
(166) 19.4 |
595 896 1010 |
(834) 214.4 |
|||
ENNG N-ethyl-N'-nitro-N-nitrosoguanidine
4NQO 4-Nitroquinoline-1-oxide
9AA 9-Aminoacridine
P Precipitate
T Partial absence of bacterial background lawn
# Standard deviation
Test Period |
From: 17 January 2010 |
To: 20 January 2010 |
||||||||||
With or without S9-Mix |
Test substance concentration (µg/plate) |
Number of revertants (mean number of colonies per plate) |
||||||||||
Base-pair substitution type |
Frameshift type |
|||||||||||
TA100 |
TA1535 |
WP2uvrA‑ |
TA98 |
TA1537 |
||||||||
+ |
0 |
77 90 77 |
(81) 7.5# |
18 16 25 |
(20) 4.7 |
46 38 47 |
(44) 4.9 |
24 29 21 |
(25) 4.0 |
19 17 16 |
(17) 1.5 |
|
+ |
50 |
90 63 71 |
(75) 13.9 |
9 9 12 |
(10) 1.7 |
34 41 49 |
(41) 7.5 |
21 25 27 |
(24) 3.1 |
10 20 12 |
(14) 5.3 |
|
+ |
150 |
97 77 C |
(87) 14.1 |
17 20 26 |
(21) 4.6 |
38 48 45 |
(44) 5.1 |
30 24 21 |
(25) 4.6 |
9 15 17 |
(14) 4.2 |
|
+ |
500 |
85 68 77 |
(77) 8.5 |
18 29 21 |
(23) 5.7 |
30 40 41 |
(37) 6.1 |
17 27 21 |
(22) 5.0 |
15 15 13 |
(14) 1.2 |
|
+ |
1500 |
80 83 94 |
(86) 7.4 |
9 19 27 |
(18) 9.0 |
47 40 36 |
(41) 5.6 |
27 28 24 |
(26) 2.1 |
12 14 12 |
(13) 1.2 |
|
+ |
5000 |
75 P 77 P 76 P |
(76) 1.0 |
22 P 22 P 21 P |
(22) 0.6 |
37 P 47 P 39 P |
(41) 5.3 |
22 P 16 P 27 P |
(22) 5.5 |
16 P 5 P 11 P |
(11) 5.5 |
|
Positive controls
S9-Mix
+ |
Name Concentration (μg/plate) No. colonies per plate |
2AA |
2AA |
2AA |
BP |
2AA |
||||||
1 |
2 |
10 |
5 |
2 |
||||||||
846 1120 1065 |
(1010) 144.9 |
187 231 228 |
(215) 24.6 |
247 276 297 |
(273) 25.1 |
97 157 152 |
(135) 33.3 |
242 290 307 |
(280) 33.7 |
|||
BP Benzo(a)pyrene
2AA 2-Aminoanthracene
C Contaminated
P Precipitate
# Standard deviation
Test Period |
From: 02 February 2010 |
To: 05 February 2010 |
||||||||||
With or without S9-Mix |
Test substance concentration (µg/plate) |
Number of revertants (mean number of colonies per plate) |
||||||||||
Base-pair substitution type |
Frameshift type |
|||||||||||
TA100 |
TA1535 |
WP2uvrA‑ |
TA98 |
TA1537 |
||||||||
- |
0 |
93 94 94 |
(94) 0.6# |
13 19 18 |
(17) 3.2 |
18 17 17 |
(17) 0.6 |
20 19 19 |
(19) 0.6 |
15 8 8 |
(10) 4.0 |
|
- |
15 |
89 98 98 |
(95) 5.2 |
19 18 16 |
(18) 1.5 |
19 19 16 |
(18) 1.7 |
15 15 16 |
(15) 0.6 |
13 15 13 |
(14) 1.2 |
|
- |
50 |
79 80 81 |
(80) 1.0 |
22 22 16 |
(20) 3.5 |
16 15 15 |
(15) 0.6 |
24 15 22 |
(20) 4.7 |
12 15 10 |
(12) 2.5 |
|
- |
150 |
83 87 87 |
(86) 2.3 |
19 19 20 |
(19) 0.6 |
16 16 15 |
(16) 0.6 |
22 18 18 |
(19) 2.3 |
12 14 12 |
(13) 1.2 |
|
- |
500 |
84 86 84 |
(85) 1.2 |
17 15 17 |
(16) 1.2 |
20 18 18 |
(19) 1.2 |
15 20 20 |
(18) 2.9 |
12 12 11 |
(12) 0.6 |
|
- |
1500 |
77 81 76 |
(78) 2.6 |
15 15 16 |
(15) 0.6 |
18 20 12 |
(17) 4.2 |
21 16 22 |
(20) 3.2 |
15 14 13 |
(14) 1.0 |
|
- |
5000 |
98 P 100 P 97 P |
(98) 1.5 |
22 P 17 P 15 P |
(18) 3.6 |
19 P 15 P 22 P |
(19) 3.5 |
22 P 22 P 16 P |
(20) 3.5 |
13 P 14 P 9 P |
(12) 2.6 |
|
Positive controls
S9-Mix
- |
Name Concentration (μg/plate) No. colonies per plate |
ENNG |
ENNG |
ENNG |
4NQO |
9AA |
||||||
3 |
5 |
2 |
0.2 |
80 |
||||||||
552 593 439 |
(528) 79.8 |
436 460 470 |
(455) 17.5 |
645 681 685 |
(670) 22.0 |
152 154 149 |
(152) 2.5 |
735 691 703 |
(710) 22.7 |
|||
ENNG N-ethyl-N'-nitro-N-nitrosoguanidine
4NQO 4-Nitroquinoline-1-oxide
9AA 9-Aminoacridine
P Precipitate
# Standard deviation
FOR REST OF RESULTS SEE OVERALL REMARKS, ATTACHMENTS
Applicant's summary and conclusion
- Conclusions:
- The test material was considered to be non-mutagenic under the conditions of this test.
This study is conducted according to an appropriate guideline and under the conditions of GLP, the study is therefore considered to be acceptable and to adequately satisfy both the guideline requirement and the regulatory requirement as a key study for this endpoint. - Executive summary:
Introduction.
The method was designed to conform to the guidelines for bacterial mutagenicity testing published by the major Japanese Regulatory Authorities including METI, MHLW and MAFF. It alsoets the requirents of the OECD Guidelines for Testing of Chemicals No. 471 "Bacterial Reverse Mutation Test", Method B13/14 of Commission Regulation (EC) number 440/2008 of 30 May 2008 and the USA, EPA (TSCA) OPPTS harmonised guidelines.
Methods.
Salmonella typhimuriumstrains TA1535, TA1537, TA98 and TA100 and Escherichia coli strain WP2uvrA-were treated with suspensions of the test material using both the Ames plate incorporation and pre-incubation methods at up to six dose levels, in triplicate, both with and without the addition of a rat liver homogenate metabolising system (10% liver S9 in standard co-factors). The dose range for the range-finding test was determined in a preliminary toxicity assay and was 50 to 5000 µg/plate. The experiment was repeated on a separate day (pre-incubation method) using fresh cultures of the bacterial strains and fresh test material formulations. The dose range was amended slightly following the results of the range-finding test and the change in test methodology and was 15 to 5000 µg/plate.
Results.
The vehicle (dimethyl sulphoxide) control plates gave counts of revertant colonies within the normal range. All of the positive control chemicals used in the test induced marked increases in the frequency of revertant colonies, both with or without metabolic activation. Thus, the sensitivity of the assay and the efficacy of the S9-mix were validated.
The test material caused a visible reduction in the growth of the bacterial background lawn of Salmonella strain TA100, without S9-mix, at 5000 µg/plate in the range-finding test only. However, this response was not observed in either the preliminary toxicity test or main test and was, therefore, considered spurious and of no biological relevance. No toxicity was noted to any of the remaining bacterial tester strains at any test material dose level in either the absence or presence of S9-mix. The test material was, therefore, tested up to the maximum recommended dose level of 5000 µg/plate. A pale, fine precipitate was observed at 5000 µg/plate, this observation did not prevent the scoring of revertant colonies.
No significant increases in the frequency of revertant colonies were recorded for any of the bacterial strains, with any dose of the test material, either with or without metabolic activation or exposure method.
Conclusion. The test material was considered to be non-mutagenic under the conditions of this test.
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