Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 221-111-2 | CAS number: 3006-86-8
- 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

Toxicity to soil macroorganisms except arthropods
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to soil macroorganisms except arthropods: long-term
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- Please refer to read-across justification attached to IUCLID Section 13.
- Reason / purpose for cross-reference:
- read-across source
- Duration:
- 28 d
- Dose descriptor:
- LC50
- Effect conc.:
- 224 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality
- Remarks on result:
- other: There was not a sufficient dose-response relationship to provide a reliable estimate and this value should be used with caution.
- Duration:
- 28 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 95.3 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mortality
- Remarks on result:
- other: The 7.5% mortality (p 0.035*) recorded at 16.3 mg a.i./kg dry soil is not considered to be biologically significant as it is an outlying result.
- Duration:
- 28 d
- Dose descriptor:
- LC50
- Effect conc.:
- 141 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- other: body weight
- Remarks on result:
- other: The confidence interval was 96.0 – 207.1 mg a.i./kg dry soil.
- Duration:
- 28 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 95.3 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- other: body weight
- Duration:
- 56 d
- Dose descriptor:
- LC50
- Effect conc.:
- 95.6 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- reproduction
- Remarks:
- number of juveniles
- Remarks on result:
- other: There was not a sufficient dose-response relationship to provide a reliable estimate and this value should be used with caution.
- Duration:
- 56 d
- Dose descriptor:
- NOEC
- Effect conc.:
- 52.9 mg/kg soil dw
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- reproduction
- Remarks:
- number of juveniles
- Remarks on result:
- other: The significant decrease observed at 16.3 mg a.i./kg dry soil is not considered of biological significance as it can be considered a result of the low level of adult mortality recorded at this rate.
Reference
Description of key information
Earthworm reprodcution test (OECD 222) with a structural analogue substance revealed a NOEC = 52.9 mg/kg soil dw.
Key value for chemical safety assessment
- Long-term EC10, LC10 or NOEC for soil macroorganisms:
- 52.9 mg/kg soil dw
Additional information
OECD 222 with CAS 6731 -36 -8
An earthworm reproduction study according to OECD 222 with a structural analogue substance (CAS 6731 -36 -8) is available. Adult mortality of 0, 0, 7.5, 5, 2.5, 2.5, 10, 95, 100 and 100% was recorded at rates of 5.04, 9.07, 16.3, 29.4, 52.9, 95.3, 171.5, 308.6, 555.6 and 1000 mg a.i./kg dry soil respectively. No mortality was recorded in the water or solvent controls. The 16.3, 171.5, 308.6, 555.6 and 1000 mg a.i./kg dry soil Trigonox 29 treated groups had significantly higher mortality than the solvent control group. The 5 mg a.i./kg dry soil Mascot Systemic treated group had significantly higher mortality than the water control group (p<0.001). The LC50 for the mortality on Day 28 was 224 mg a.i./kg dry soil. However, there was not a sufficient dose-response relationship to provide a reliable estimate and this value should be used with caution. The NOEC for mortality on Day 28 was 95.3 mg a.i./kg dry soil. The 7.5% mortality (p 0.035*) recorded at 16.3 mg a.i./kg dry soil is not considered to be biologically significant as it is an outlying result. The Trigonox 29 treated groups at 555.6 and 1000 mg a.i./kg dry soil were excluded from the analysis of body weight for adult earthworms as there were no surviving earthworms on Day 28. The 171.5 and 308.6 mg a.i./kg dry soil Trigonox 29 treated groups had significantly lower adult bodyweight than the solvent control group (p<0.001). The 5 mg a.i./kg dry soil Mascot Systemic treated group had significantly lower adult bodyweight than the water control group (p<0.001).
The LC50 for the mean body weight of the adult earthworms at Day 28 was 141.0 mg a.i/kg dry soil. The confidence interval was 96.0 – 207.1 mg a.i./kg dry soil.
The NOEC for the mean bodyweight at Day 28 was 95.3 mg a.i./kg dry soil. The Trigonox 29 treated groups at 308.5, 555.6 and 1000 mg a.i./kg dry soil and the positive control group were excluded from the analysis of number of juveniles on Day 56 as there were only two surviving earthworms at 308.5 mg a.i./kg dry soil and none at 555.6 and 1000 mg a.i./kg dry soil. No juveniles were produced in the Mascot Systemic treatment.
The coefficient of variation of the number of juveniles in the solvent control group was 4.39%. The 16.3, 95.3 and 171.5 mg a.i./kg dry soil Trigonox 29 treated groups had significantly fewer juveniles than the solvent control group (p=0.042). The 29.4 and 52.9 mg a.i./kg dry soil Trigonox 29 treated groups had significantly more juveniles than the solvent control group (p=0.042). The water control group had significantly fewer juveniles than the solvent control group (p=0.005).
The LC50 for the number of juveniles on Day 56 was 95.6 mg a.i./kg dry soil. However, there was not a sufficient dose-response relationship to provide a reliable estimate and this value should be used with caution.
The NOEC for the number of juvenile worms on Day 56 was 52.9 mg a.i./kg dry soil. The significant decrease observed at 16.3 mg a.i./kg dry soil is not considered of biological significance as it can be considered a result of the low level of adult mortality recorded at this rate. The study was considered valid as there was ≤ 10% adult mortality at four weeks and ≥30 juveniles had been produced in each water control replicate by the end of the test with the coefficient of variation of reproduction ≤ 30%. In addition application of the toxic reference Mascot Systemic at 5 mg a.i./kg dry soil resulted in substantial and unequivocal toxic effects.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.