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EC number: 206-354-4 | CAS number: 330-54-1
- 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:
- Mar 1984
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Comparable to guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 984
- Report date:
- 1984
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 471 (Bacterial Reverse Mutation Assay)
- GLP compliance:
- not specified
- Type of assay:
- bacterial reverse mutation assay
Test material
- Reference substance name:
- Diuron
- EC Number:
- 206-354-4
- EC Name:
- Diuron
- Cas Number:
- 330-54-1
- Molecular formula:
- C9H10Cl2N2O
- IUPAC Name:
- 3-(3,4-dichlorophenyl)-1,1-dimethylurea
- Details on test material:
- - Physical state: solid
- Analytical purity: 98.8%
- Lot/batch No.: 232114080
- Stability under test conditions: yes
Constituent 1
Method
- Target gene:
- not applicable
Species / strain
- Species / strain / cell type:
- S. typhimurium TA 1535, TA 1537, TA 98 and TA 100
- Metabolic activation:
- with and without
- Metabolic activation system:
- S9-mix (induced with Aroclor 1254) from rats
- Test concentrations with justification for top dose:
- 0, 125, 250, 500, 1000, 2000 µg/plate per strain
- Vehicle / solvent:
- - Vehicle(s)/solvent(s) used: DMSO
Controls
- Untreated negative controls:
- no
- Negative solvent / vehicle controls:
- no
- True negative controls:
- no
- Positive controls:
- yes
- Positive control substance:
- other: Cyclophosphamide, Trypaflavine and 2-Aminoanthracene
- Details on test system and experimental conditions:
- METHOD OF APPLICATION: in agar (plate incorporation)
DURATION
- no Preincubation period
- Exposure duration: 48 h at 37 °C
NUMBER OF CELLS EVALUATED:
minimal culture density: approx. 0.1 x 10 to the power 7 CFU/mL;
approx. maximum: 4 x 10 to the power of 9 CFU/mL
DETERMINATION OF CYTOTOXICITY
performed between 0 to 12500 µg/plate
OTHER: 4 plates per strain and dose, both with and without metabolic activation; same number of vehicle controls; - Evaluation criteria:
- A reproducible, dose-related increase in the mutant counts of at least one strain is considered positive , and about double the negative control should be reached
- Statistics:
- The ANOVA model was used for calculations
Results and discussion
Test results
- 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:
- cytotoxicity
- Remarks:
- For strains TA 98, 1535 and 1537 cytotoxicity was observed at 500 µg/plate and above with and without metabolic activation. For strain TA 100 cytotoxicity was revealed at 2500 µg/plate and above with and without metabolic activation
- Vehicle controls validity:
- valid
- Untreated negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- ADDITIONAL INFORMATION ON CYTOTOXICITY:
The two highest dose levels (1000 and 2000 µg/plate) were toxic as evidenced by thinning bacterial lawn and/or reduced revertant count - 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 cytotoxicity testing (mean of 4 countings)
|
Without S9-mix |
With S9-mix |
||||||
µg/plate |
TA100 |
TA1535 |
TA98 |
TA1537 |
TA100 |
TA1535 |
TA98 |
TA1537 |
0 |
100 |
28 |
18 |
6 |
135 |
17 |
33 |
6 |
20 |
100 |
35 |
20 |
5 |
127 |
8 |
35 |
8 |
100 |
80 |
29 |
19 |
4 |
107 |
15 |
29 |
7 |
500 |
62 |
B |
B |
B |
123 |
12 |
24 |
5 |
2500 |
B |
B |
B |
0 |
37 |
B |
B |
B |
12500 |
P |
P |
P |
P |
P |
P |
P |
P |
2-AA |
138 |
20 |
40 |
12 |
1284 |
344 |
669 |
92 |
Endoxan |
n.p. |
32 |
n.p. |
n.p. |
n.p. |
458 |
n.p. |
n.p. |
Endoxan |
96 |
n.p. |
n.p. |
n.p. |
621 |
n.p. |
n.p. |
n.p. |
Trypaflav. |
n.p. |
n.p. |
87 |
64 |
n.p. |
n.p. |
2895 |
971 |
B - background growth
P - precipitation
n.p. - not performed
Table 2: Results of mutagenicity testing (mean of 4 countings)
Strain TA 1535 |
||||
µg / Plate |
Mutants / Plate |
Bact./ml |
||
- S 9 |
+ S 9 |
Exp. +8 |
||
0 |
30±4 |
14±2 |
42.2 |
|
125 |
33±5 |
11±4 |
41.4 |
|
250 |
20±2 |
13±3 |
34.9 |
|
500 |
b** |
9±3 |
38.3 |
|
1000 |
0±0 |
5±2 |
6.0 ** |
|
2000 |
0±0 |
b |
0.9 ** |
|
Endoxan, 145µg |
31±7 |
205±9 |
40.7 |
|
2-AA, 3 µg |
31±6 |
231±28 |
37.8 |
|
Strain TA 100 |
||||
0 |
110±11 |
132±13 |
35.4 |
|
125 |
103±15 |
106±9 |
28.6 |
|
250 |
90±10 |
132±11 |
9.3** |
|
500 |
41±6 |
91±21 |
7.2** |
|
1000 |
b |
70±17 |
0.9 ** |
|
2000 |
b |
25 p±8 |
0.3 ** |
|
Endoxan, 290µg |
130±11 |
398±36 |
37.4 |
|
2-AA, 3 µg |
133±18 |
1017±166 |
35.2 |
|
Strain TA 1537 |
||||
0 |
8±3 |
9±1 |
32.7 |
|
125 |
3±1 |
9±3 |
30.7 |
|
250 |
b |
7±1 |
18.6** |
|
500 |
3±3 |
4±2 |
2.5** |
|
1000 |
0±0 |
2±2 |
0.1 ** |
|
2000 |
0±0 |
3 p±2 |
< 0.1 ** |
|
T.flavin, 50µg |
54±14 |
336±33 |
28.3 |
|
2-AA, 3 µg |
11±3 |
74±5 |
34.4 |
|
Strain TA 98 |
||||
0 |
27±5 |
26±6 |
34.8 |
|
125 |
17±3 |
31±2 |
31.8 |
|
250 |
9±5 |
31±7 |
9.1** |
|
500 |
b |
24±6 |
2.3** |
|
1000 |
0±0 |
25±6 |
0.2** |
|
2000 |
0±0 |
9 p±5 |
0.2** |
|
T.flavin, 50µg |
51±15 |
816±51 |
31.4 |
|
2-AA, 3µg |
43±7 |
316±50 |
40.7 |
**- background
b - bactericidal effect
p - precipitation
The two highest dose levels (1000 and 2000 µg/plate) were toxic as evidenced by thinning bacterial lawn and/or reduced revertant count. Diuron did not increase the number of revertant colonies at any exposure level, with or without activation .No dose-related increase in mutant colonies was observed. The sensitivity of the test system was evidenced by concurrent positive controls.
Applicant's summary and conclusion
- Conclusions:
- Interpretation of results (migrated information):
negative - Executive summary:
A reliable genetic toxicity in vitro study was performed according to Ames (1975).Diuron was applied in concentrations of 0, 125, 250, 500, 1000, and 2000 µg/plate. Diuron was not mutagenic in the four tested Salmonella strains up to toxic concentrations both in the presence and absence of a rat metabolic activation system under the conditions employed. (Herbold 1984)
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