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EC number: 203-921-8 | CAS number: 111-92-2
- 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 mammalian cells
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 476 (In Vitro Mammalian Cell Gene Mutation Test using the Hprt and xprt genes)
- GLP compliance:
- yes
- Type of assay:
- in vitro mammalian cell gene mutation test using the Hprt and xprt genes
Test material
- Reference substance name:
- Dibutylamine
- EC Number:
- 203-921-8
- EC Name:
- Dibutylamine
- Cas Number:
- 111-92-2
- Molecular formula:
- C8H19N
- IUPAC Name:
- N-butylbutan-1-amine
- Details on test material:
- Di-n-butylamine
Constituent 1
Method
- Target gene:
- hypoxanthine-guanine phosphoribosyl transferase
Species / strain
- Species / strain / cell type:
- mouse lymphoma L5178Y cells
- Details on mammalian cell type (if applicable):
- - Type and identity of media: RPMI 1640 media
- Periodically checked for Mycoplasma contamination: yes
- Metabolic activation:
- with and without
- Metabolic activation system:
- rat S9 mix
- Test concentrations with justification for top dose:
- Range finder: 0; 40.41; 80.81; 161.6; 323.3; 646.5; 1293 µg/ml (with and without S9 mix)
Experiment 1: 0, 50, 100, 150, 240, 280, 320, 360 µg/ml (without S9 mix)
0, 80, 160, 240, 280, 400, 450, 525 µg/ml (with S9 mix)
Experiment 2: 0, 50, 100, 150, 250, 300, 320, 340, 360, 400, 450 µg/ml (without S9mix)
0, 100, 200, 300, 350, 400, 450, 500, 525, 550,600 µg/ml (with S9 mix) - Vehicle / solvent:
- - Vehicle(s)/solvent(s) used: ethanol
Controls
- Untreated negative controls:
- yes
- Negative solvent / vehicle controls:
- yes
- Positive controls:
- yes
- Positive control substance:
- other: see remarks
- Remarks:
- 4-nitroquinoline 1-oxide 0.10/0.15 µg/ml without S9 mix; benzo[a]pyrene 2.00/3.00 µg/ml
- Details on test system and experimental conditions:
- METHOD OF APPLICATION:
- in medium
DURATION
- Exposure duration: 3 h
- Expression time (cells in growth medium): 7 days
NUMBER OF REPLICATIONS: 2 - Evaluation criteria:
- For valid data, the test article was considered to induce forward mutation at the hprt locus in mouse lymphoma L5178Y cells if:
1.The mutant frequency at one or more concentrations was significantly greater than that of the negative control (p≤ 0.05)
2.There was a significant concentration relationship as indicated by the linear trend analysis (p≤ 0.05)
3.The effects described above were reproducible. Results that only partially satisfied the assessment criteria described above were considered on a case-by-case basis. - Statistics:
- Statistical significance of mutant frequencies was carried out according to the UKEMS guidelines. The control log mutant frequency (LMF) was copared with the LMF from each treatment concentration and the data were checked for a linear trend in mutant frequency with test article treatment. These tests require the calculation of the heterogeneity factor to obtain a modified estimate of variance.
Results and discussion
Test results
- Species / strain:
- mouse lymphoma L5178Y cells
- Metabolic activation:
- with and without
- Genotoxicity:
- negative
- Cytotoxicity / choice of top concentrations:
- no cytotoxicity
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- valid
- Positive controls validity:
- valid
- Additional information on results:
- In the cytotoxicity Range-Finder Experiment, six concentrations were tested in the absence and presence of S-9 ranging from 40.41 to 1293 µg/mL (equivalent to 10 mM at the highest concentration tested). The highest concentration tested (1293 µg/mL) was not plated due to excessive toxicity and complete toxicity (0% RS) was observed at the highest concentration plated in the absence and presence of S-9 (646.5 µg/mL). The highest concentration to provide >10% RS was 323.3 µg/mL in the absence and presence of S-9, which gave 12% and 37% RS, respectively.
No marked changes in osmolality were observed in the Range-Finder at the highest concentration tested (1293 µg/mL) as compared to the concurrent vehicle controls (individual data not reported). Marked changes in pH were observed at 1293 µg/mL as compared to the concurrent vehicle controls but no marked changes were observed up to 646.5 µg/mL (individual data not reported). As no concentration tested in the Mutation Experiments was greater than 600 µg/mL no further measurements were performed.
Any other information on results incl. tables
In Experiment 1 ten concentrations, ranging from 50 to 500 µg/mL in the absence of S‑9 and from 80 to 600 µg/mL in the presence of S‑9, were tested. Seven days after treatment, the highest two concentrations tested in the absence of S‑9 (400 and 500 µg/mL) and the highest concentration tested in the presence of S‑9 (600 µg/mL) were considered too toxic for selection to determine viability and 6TG resistance. In addition, concentrations of 200 µg/mL in the absence of S‑9 and 320 and 360 µg/mL in the presence of S‑9 were not selected as there were sufficient non-toxic concentrations. All other concentrations were selected in the absence and presence of S‑9. The highest concentrations plated were 360 µg/mL in the absence of S‑9 and 525 µg/mL in the presence of S‑9, which gave 18% and 22% RS in the absence and presence of S-9, respectively. Although no concentration tested in the presence of S-9 gave the desired 10 to 20% RS the toxicity level observed at 525 µg/mL (22% RS) was sufficiently close to 10 to 20% RS to be considered acceptable and the data are therefore considered valid.
In Experiment 2 ten concentrations, ranging from 50 to 450 µg/mL in the absence of S‑9 and from 100 to 600 µg/mL in the presence of S‑9, were tested. Seven days after treatment all concentrations in the absence and presence of S-9 were selected to determine viability and 6TG resistance. The highest concentrations tested, 450 µg/mL in the absence of S‑9 and 600 µg/mL in the presence of S‑9, gave 26% and 20% RS in the absence, respectively (seeTable8). It may be noted that in the absence of S‑9 a concentration of 400 µg/mL gave 20% RS and the data are therefore considered valid.
Experiment 1 (3 hour treatment in the absence and presence of S-9)
Treatment (µg/mL) |
-S-9 |
Treatment (µg/mL) |
+S-9 |
||||||
|
%RS |
MF§ |
|
%RS |
MF§ |
||||
0 |
|
100 |
1.71 |
|
0 |
|
100 |
2.62 |
|
50 |
|
94 |
3.38 |
NS |
80 |
|
78 |
1.18 |
NS |
100 |
|
73 |
2.49 |
NS |
160 |
|
74 |
1.75 |
NS |
150 |
|
64 |
2.19 |
NS |
240 |
|
59 |
2.60 |
NS |
240 |
|
58 |
1.63 |
NS |
280 |
|
52 |
1.90 |
NS |
280 |
|
54 |
2.28 |
NS |
400 |
|
44 |
2.49 |
NS |
320 |
|
30 |
1.69 |
NS |
450 |
|
32 |
1.79 |
NS |
360 |
|
18 |
1.81 |
NS |
525 |
|
22 |
1.78 |
NS |
Linear trend |
NS |
Linear trend |
NS |
||||||
NQO |
|
|
|
|
B[a]P |
|
|
|
|
0.1 |
|
62 |
24.79 |
|
2 |
|
54 |
32.03 |
|
0.15 |
|
73 |
16.36 |
|
3 |
|
39 |
58.99 |
|
Experiment 2 (3 hour treatment in the absence and presence of S-9)
Treatment (µg/mL) |
-S-9 |
Treatment (µg/mL) |
+S-9 |
||||||
|
%RS |
MF§ |
|
%RS |
MF§ |
||||
0 |
|
100 |
2.19 |
|
0 |
|
100 |
1.18 |
|
50 |
|
97 |
1.55 |
NS |
100 |
|
94 |
1.36 |
NS |
100 |
|
90 |
1.55 |
NS |
200 |
|
81 |
1.45 |
NS |
150 |
|
82 |
2.76 |
NS |
300 |
|
69 |
2.42 |
NS |
250 |
|
51 |
3.65 |
NS |
350 |
|
65 |
3.61 |
NS |
300 |
|
54 |
2.46 |
NS |
400 |
|
68 |
4.32 |
NS |
320 |
|
47 |
5.65 |
NS |
450 |
|
52 |
2.67 |
NS |
340 |
|
58 |
0.60 |
NS |
500 |
|
34 |
1.51 |
NS |
360 |
|
45 |
4.60 |
NS |
525 |
|
35 |
2.02 |
NS |
400 |
|
20 |
3.06 |
NS |
550 |
|
25 |
2.98 |
NS |
450 |
|
26 |
2.54 |
NS |
600 |
|
20 |
2.45 |
NS |
Linear trend |
NS |
Linear trend |
* |
||||||
NQO |
|
|
|
|
B[a]P |
|
|
|
|
0.1 |
|
86 |
12.51 |
|
2 |
|
39 |
25.22 |
|
0.15 |
|
58 |
15.93 |
|
3 |
|
18 |
26.40 |
|
§ 6-TG resistant mutants/106viable cells 7 days after treatment
%RS Percent relative survival adjusted by post treatment cell counts
NS Not significant
*, **, *** Test for linear trend: χ2(one-sided), significant at 5%, 1% and 0.1% level respectively
Applicant's summary and conclusion
- Conclusions:
- A GLP-compliant study according to OECD 476 was performed. It is concluded that the test substance did not induce mutation at the hprt locus of L5178Y mouse lymphoma cells when tested under the conditions employed in this study.
- Executive summary:
A GLP-compliant in vitro mammalian cell gene mutation test using the Hprt and xprt genes according to OECD 476 was performed. In the cytotoxicity Range-Finder Experiment, six concentrations were tested in the absence and presence of rat S9 ranging from 40.41 to 1293 µg/mL (equivalent to 10 mM at the highest concentration tested). The highest concentration tested (1293 µg/mL) was not plated due to excessive toxicity and complete toxicity (0% RS) was observed at the highest concentration plated in the absence and presence of rat S9 (646.5 µg/mL). The highest concentration to provide >10% RS was 323.3 µg/mL in the absence and presence of rat S9, which gave 12% and 37% RS, respectively.
No marked changes in osmolality were observed in the Range-Finder at the highest concentration tested (1293 µg/mL) as compared to the concurrent vehicle controls (individual data not reported). Marked changes in pH were observed at 1293 µg/mL as compared to the concurrent vehicle controls but no marked changes were observed up to 646.5 µg/mL (individual data not reported). As no concentration tested in the Mutation Experiments was greater than 600 µg/mL no further measurements were performed.
In Experiment 1 ten concentrations, ranging from 50 to 500 µg/mL in the absence of rat S9 and from 80 to 600 µg/mL in the presence of rat S9, were tested. Seven days after treatment, the highest two concentrations tested in the absence of rat S9 (400 and 500 µg/mL) and the highest concentration tested in the presence of rat S9 (600 µg/mL) were considered too toxic for selection to determine viability and 6TG resistance. In addition, concentrations of 200 µg/mL in the absence of rat S9 and 320 and 360 µg/mL in the presence of rat S9 were not selected as there were sufficient non-toxic concentrations. All other concentrations were selected in the absence and presence of rat S9. The highest concentrations plated were 360 µg/mL in the absence of rat S9 and 525 µg/mL in the presence of rat S9, which gave 18% and 22% RS in the absence and presence of rat S9, respectively. Although no concentration tested in the presence of rat S9 gave the desired 10 to 20% RS the toxicity level observed at 525 µg/mL (22% RS) was sufficiently close to 10 to 20% RS to be considered acceptable and the data are therefore considered valid.
In Experiment 2 ten concentrations, ranging from 50 to 450 µg/mL in the absence of rat S9 and from 100 to 600 µg/mL in the presence of rat S9, were tested. Seven days after treatment all concentrations in the absence and presence of rat S9 were selected to determine viability and 6TG resistance. The highest concentrations tested, 450 µg/mL in the absence of rat S9 and 600 µg/mL in the presence of rat S9, gave 26% and 20% RS in the absence, respectively (seeTable8). It may be noted that in the absence of rat S9 a concentration of 400 µg/mL gave 20% RS and the data are therefore considered valid.
It is concluded that the test substance did not induce mutation at the hprt locus of L5178Y mouse lymphoma cells when tested under the conditions employed in this study. These conditions included treatments up to toxic concentrations in two independent experiments in the absence and presence of a rat liver metabolic activation system (S9).
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