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EC number: 214-494-2 | CAS number: 1135-66-6
- 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 aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- calculation (if not (Q)SAR)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Data is from computational model developed by USEPA
- Justification for type of information:
- Data is from computational model developed by USEPA
- Qualifier:
- according to guideline
- Guideline:
- other: Modeling database
- Principles of method if other than guideline:
- ECOSAR estimates log Kow values using the US EPA's KOWWIN Program for aquatic toxicity.Toxicity of a chemical was measured on the basis of similarity of structure to chemicals for which the aquatic toxicity has been previously measured by structure-activity relationships (SARs) program based upon the octanol /water partition coefficient (Kow). Data from ECOSAR class,neutral organics was used.
The estimation methods in EPI Suite™ have been developed by government, academic, and private sector researchers over many years and represent some of the best techniques currently available. The intended application domain of EPI Suite is organic chemicals, and inorganic as well as organometallic chemicals generally can be considered outside the domain. - GLP compliance:
- no
- Specific details on test material used for the study:
- - Name of test material (IUPAC name): (2S)-1,3,4,5,6,7-hexahydro-1,1,5,5-tetramethyl-2H-2,4a-methanonaphthalene
- IUPAC name: (2S)-1,3,4,5,6,7-hexahydro-1,1,5,5-tetramethyl-2H-2,4a-methanonaphthalene
- Moleuclar formula: C15H24
- Molecular weight: 204.3546 g/mol
- Substance type: Organic
- Smiles: CC1(C)CCC=C2C(C)(C)[C@H]3CC[C@@]12C3
- Inchi: 1S/C15H24/c1-13(2)8-5-6-12-14(3,4)11-7-9-15(12,13)10-11/h6,11H,5,7-10H2,1-4H3/t11-,15-/m0/s1
- Physical state: liquid - Analytical monitoring:
- not required
- Vehicle:
- not specified
- Test organisms (species):
- Daphnia magna
- Test type:
- not specified
- Water media type:
- not specified
- Total exposure duration:
- 48 h
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 0.055 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- test mat.
- Basis for effect:
- not specified
- Remarks on result:
- other: Neutral Organics
- Validity criteria fulfilled:
- not specified
- Conclusions:
- On the basis of EPI suite, ECOSAR version 1.1, the LC 50 value for short term toxicity to aquatic invertebrates was predicted to be 0.055 mg/l for test material in 48 hrs.
Based on this value it can be concluded that the substance is considered to be toxic to aquatic environment and can be classified in aquatic acute 1 category as per the criteria mentioned in CLP regulation. - Executive summary:
Based on the prediction done by EPI suite, ECOSAR version 1.1, on the basis of similarity of structure to chemicals for which the aquatic toxicity has been previously measured by structure-activity relationships (SARs) program, the LC 50 value for short term toxicity to aquatic invertebrates was predicted.
On the basis of this program, the LC 50 value for short term toxicity to aquatic invertebrates was predicted to be 0.055 mg/l for test material in 48 hrs.
Based on this value it can be concluded that the substance is considered to be toxic to aquatic environment and can be classified in aquatic acute 1 category as per the criteria mentioned in CLP regulation.
Reference
Description of key information
Toxicity to aquatic invertebrate:
Based on the prediction done by EPI suite, ECOSAR version 1.1, on the basis of similarity of structure to chemicals for which the aquatic toxicity has been previously measured by structure-activity relationships (SARs) program, the LC 50 value for short term toxicity to aquatic invertebrates was predicted.
On the basis of this program, the LC 50 value for short term toxicity to aquatic invertebrates was predicted to be0.055mg/l for test materialin 48 hrs.
Based on this value it can be concluded that the substance is considered to be toxic to aquatic environment and can be classified in aquatic acute 1 category as per the criteria mentioned in CLP regulation.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 0.55 mg/L
Additional information
Toxicity to aquatic invertebrate:
Based on the prediction done by EPI suite, ECOSAR version 1.1, on the basis of similarity of structure to chemicals for which the aquatic toxicity has been previously measured by structure-activity relationships (SARs) program, the LC 50 value for short term toxicity to aquatic invertebrates was predicted.
On the basis of this program, the LC 50 value for short term toxicity to aquatic invertebrates was predicted to be0.055mg/l for test materialin 48 hrs.
Based on this value it can be concluded that the substance is considered to be toxic to aquatic environment and can be classified in aquatic acute 1 category as per the criteria mentioned in CLP regulation.
The above predicition was supported by the data from authorative databases
1)To study the effects of test material on aquatic invertebrate test was carried for 48 H under static condition. Increasing trend of Intoxication (immobile) was measured during the test.Effective concentration EC50 to 50% of Daphnia pulex when exposed to test material for 48 h is 0.044 mg/L. It can be concluded from the EC50 Intoxication value that the test material is toxic to the aquatic invertebrateand can be considered as “Aquatic acute 1” as per the classification criteria for aquatic environment.
2)To study the effects of [1S-(1α,3aβ,4α,8aβ)]-decahydro-4,8,8-trimethyl-9-methylene-1,4-methanoazulene on aquatic invertebrate test was carried for 48 H under static condition. Increasing trend of Intoxication (immobile) was measured during the test.
Effective concentration EC50 to 50% of Daphnia pulex when exposed to 1S-(1α,3aβ,4α,8aβ)]-decahydro-4,8,8-trimethyl-9-methylene-1,4-methanoazulene for 48 h is 0.08 mg/L. It can be concluded from the EC50 Intoxication value that the 1S-(1α,3aβ,4α,8aβ)]-decahydro-4,8,8-trimethyl-9-methylene-1,4-methanoazulene is toxic to the aquatic invertebrateand can be considered as “Aquatic acute 1” as per the classification criteria for aquatic environment.
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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