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EC number: 406-140-2 | CAS number: 114369-43-6 INDAR
- 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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1988-04 to 1988-08
- Reliability:
- 1 (reliable without restriction)
- Qualifier:
- according to guideline
- Guideline:
- EPA OPP 72-1 (Fish Acute Toxicity Test)
- Deviations:
- not specified
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- yes
- Vehicle:
- yes
- Remarks:
- Acetone
- Details on test solutions:
- A diluter stock solution (38000 mg a.s./l) was prepared by dissolving 3.93 g of RH-7592 Technical in acetone. The injector volume was adjusted to deliver 0.2 ml of stock to 1.9 L of dilution volume. The resulting nominal concentration regime of RH-7592 Technical was 0.25, 0.50, 1.0, 2.0 and
4.0 mg a.s./L. The solvent control chamber received acetone at 0.1 mL/L, acetone : water ratio. - Test organisms (species):
- Lepomis macrochirus
- Details on test organisms:
- In-house culture
- Test type:
- flow-through
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Test temperature:
- 21 to 23°C
- pH:
- 7.3 to 8.1
- Dissolved oxygen:
- 7.4 to 9.3 mg O2/L
- Details on test conditions:
- The acute lethal toxicity of fenbuconazole to bluegill sunfish (Lepomis macrochirus) was assessed in a 96 hour test, conducted under flow-through conditions, with fish of mean weight 0.21 ± 0.042 g and mean length of 22 ± 1.3 mm. Duplicate groups of ten fish were exposed to a nominal test series of 0.0 (control), 0.0 (0.1 mL acetone/L solvent control), 0.25, 0.50, 1.0, 2.0 and 4.0 mg a.s./L (adjusted for purity). The test vessel volume was 15 liters. he test was conducted at 21 to 23°C with dissolved oxygen levels of 7.4 to 9.3 mg O2/L (87 to 109% of saturation) and at a pH of 7.3 to 8.1. The dilution water was well water.
Exposure levels were monitored by measuring fenbuconazole in samples of test media collected at 0 and 96 hours. An HPLC/UV method of analysis was employed with detection at a wavelength of 220 nm. Measured concentrations at 0-hours were 0.13, 0.18, 0.39, 0.83, and 1.9 mg a.s./L for levels 1-5, respectively. Measured concentrations at 96-hours were 0.13, 0.19, 0.46, 1.0, and 2.6 mg/L for levels 1-5, respectively. No residues of fenbuconazole were detected in the control and solvent control at concentrations greater than the limit of detection (0.058 mg/L) during the study. The mean measured concentrations were 0.13, 0.18, 0.42, 0.92 and 2.2 mg a.s./L (36 to 55% of the nominal concentrations). A white precipitate was noted in the diluter mixing cell and in all test levels after 24 hours indicating incomplete solubility at all concentrations. Concentrations were consistent throughout the study but below 80% of nominal therefore, the mean-measured concentrations were used to determine toxicity values. - Duration:
- 96 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 0.42 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Key result
- Duration:
- 96 h
- Dose descriptor:
- EC50
- Effect conc.:
- 0.68 mg/L
- Nominal / measured:
- meas. (not specified)
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Details on results:
- Eighteen of twenty fish died in the 0.92 mg/L treatment and twenty of twenty fish died in the 2.2 mg/L treatment after 96-hours of exposure. There was no mortality in any other treatment or in the controls. Signs of toxicity, such as loss of equilibrium, surfacing and quiescence were noted at the 0.92 mg/L treatment level. A precipitate was noted in concentrations =0.42 mg/L at 24-hours and in concentrations =0.13 mg/L for the remainder of the test. The 96h LC50 for fenbuconazole was determined by binomial calculation to be 0.68 mg/L, measured, with 95% confidence limits of 0.42-0.92 mg/L. The NOEC was considered to be 0.42 mg/L (measured) based on the lack of sublethal effects at this and all lower concentrations. The slope of the 96-hour dose-response line was 7.5.
- Sublethal observations / clinical signs:
Table 1: Mortality data
Nominal concentration
Mean measured concentration
Mortality
(mg/L)
(mg/L)
24 h
48 h
72 h
96 h
Control
ND (<0.058)
0
0
0
0
Solvent control
ND (<0.058)
0
0
0
0
0.25
0.13
0
0
0
0
0.50
0.18
0
0
0
0
1.0
0.42
0
0
0
0
2.0
0.92
10/20*
13/20*
17/20*
18/20*
4.0
2.2
20/20
20/20
20/20
20/20
* signs of toxicity observed in surviving fish
- Validity criteria fulfilled:
- yes
- Conclusions:
- The LC50 (96h) of the test was 0.68 mg/L
The NOEC of the test item was 0.42 mg/L - Executive summary:
The 96h LC50 of fenbuconazole to bluegill sunfish (Lepomis macrochirus) was 0.68 mg a.s./L, mean measured. The NOEC was 0.42 mg a.s./L, mean measured, based on the lack of sublethal effects at this and all lower concentrations.
Reference
Description of key information
The 96h LC50 of fenbuconazole to bluegill sunfish (Lepomis macrochirus) was 0.68 mg a.s./L, mean measured.
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Dose descriptor:
- LC50
- Effect concentration:
- 0.68 mg/L
Additional information
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.
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