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EC number: 218-691-4 | CAS number: 2216-52-6
- 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:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Remarks:
- for read across
- Justification for type of information:
- Data for the target chemical is summarized based on the structurally similar read across chemicals
- Reason / purpose for cross-reference:
- read-across source
- Reason / purpose for cross-reference:
- read-across source
- Qualifier:
- according to guideline
- Guideline:
- other: as mentioned below
- Principles of method if other than guideline:
- WoE report is based on two short term toxicity study of invertebrate for the test chemical :1.To evaluate short term toxicity of test material on Biomphalaria alexandrina
- GLP compliance:
- not specified
- Vehicle:
- not specified
- Details on test solutions:
- 1. Stock solution of test chemical was initially dissolved in dimethylsulfoxide (DMSO) to enhance the solubility, and serially diluted further with dechlorinated distilled water to achieve the desired series of concentrations. The final DMSO concentration in the experiments never exceeded 0.5% (v/v), and an equal amount was added to the control
- Test organisms (species):
- other: 1. Biomphalaria alexandrina 2. Daphnia magna
- Details on test organisms:
- 1.- Common name: freshwater snail-8.072mm shell diameter- Source: The snails were collected from fresh water ponds (untreated with molluscicides) located at Bardalah village- Acclimation conditions (same as test or not): Specimens were acclimated to laboratory conditions in a glass aquarium containing 5 l ofdechlorinated tap water.- Food type: fed on dry lettuce leaves-oxygenated for 1 h daily, for 1 week prior to experimentation.-Number of organism : 62.- Source: D. magna were obtained from Dr. Freda Taub at the University of Washington-Age: 24 hr old-food : Daphnid stock cultures were fed a mixture of A. falcatus, S. capricornutum, and Chlamydomonas reinhardi 90
- Test type:
- static
- Water media type:
- freshwater
- Total exposure duration:
- 48 h
- Remarks on exposure duration:
- 24 and 48 hr
- Hardness:
- 1)136 mg/l (as CaCO3)2) 132 ppm total CaCO3
- Test temperature:
- 1) 25 °C
- pH:
- 1) 7.32) 7.2-7.5
- Dissolved oxygen:
- 1) 6.8 mg/l.
- Conductivity:
- 1) 352 µmΩ/cm
- Details on test conditions:
- 1) - Common name: freshwater snail-8.072mm shell diameter- Source: The snails were collected from fresh water ponds (untreated with molluscicides) located at Bardalah village- Acclimation conditions (same as test or not): Specimens were acclimated to laboratory conditions in a glass aquarium containing 5 l ofdechlorinated tap water.- Food type: fed on dry lettuce leaves-oxygenated for 1 h daily, for 1 week prior to experimentation.-Number of organism : 62) - Test vessel: 250-mL glass beakers-Fill volume: 100 mL of the test solution- No. of vessels per control (replicates): 2- Photoperiod : light-dark cycle of 16:8 hr
- Reference substance (positive control):
- not specified
- Duration:
- 24 h
- Dose descriptor:
- LC50
- Effect conc.:
- 101.59 mg/L
- Nominal / measured:
- not specified
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 276 mg/L
- Nominal / measured:
- not specified
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Reported statistics and error estimates:
- 1.All data were subjected to analysis of variance (ANOVA) and means of LC50 values were compared for significance at the probability of 0.052.The effective concentrations at which 50% of the organisms are immobilized (EC50) were computed using the probit analysis
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The test chemical (+)-Neomenthol is not likely to be toxic to fish atleast in the concentration range of 101.50 - 276.0 mg/l
- Executive summary:
Data available for the structurally and functionally similar read across chemicals has been reviewed to determine the short term toxicity of aquatic invertebrate of the test chemical (+)-Neomenthol (2216 -52 -6).The studies are as mentioned below:
1. The short term toxicity study of test material was evaluated for aquatic invertebrate Biomphalaria alexandrina snails .
The snails were collected from fresh water ponds (untreated with molluscicides). Specimens were acclimated to laboratory conditions in a glass aquarium containing 5 l of dechlorinated tap water, fed on dry lettuce leaves and oxygenated for 1 h daily, for 1 week prior to experimentation. The median lethal effect concentration (LC50) for 24 h was observed to be 101.59 mg/l (with 95% confidence limits 89.45 – 115.4).
2. Short term toxicity of test material was evaluated for test material Ten neonates less than 24 hr old Daphnids were used for the test . Daphnid stock cultures were fed a mixture of A. falcatus, S. capricornutum, and Chlamydomonas reinhardi 90.
Two replicates were used in each test. Daphnia were gently touched with a pastier pipet at 24 and 48 hr.If the daphnia could not swim actively for 15 s, immobilization (mortality) was recorded. The effective concentrations at which 50% of the organisms are immobilized (EC50) were computed using the probit analysis. The effect concentration of test chemical (EC50) for 50% immobilization of Daphnia magna was observed to be 276.0 mg/l.
On the basis of above effect concentration it can be considered that the test material has no toxic effect on aquatic invertebrates and cannot be classified as per CLP criteria.
Reference
Description of key information
Short term toxicity to aquatic invertebrate:
Data available for the structurally and functionally similar read across chemicals has been reviewed to determine the short term toxicity of aquatic invertebrate of the test chemical (+)-Neomenthol (2216 -52 -6).The studies are as mentioned below:
1. The short term toxicity study of test material was evaluated for aquatic invertebrate Biomphalaria alexandrina snails .
The snails were collected from fresh water ponds (untreated with molluscicides). Specimens were acclimated to laboratory conditions in a glass aquarium containing 5 l of dechlorinated tap water, fed on dry lettuce leaves and oxygenated for 1 h daily, for 1 week prior to experimentation.The median lethal effect concentration (LC50) for 24 h was observed to be 101.59 mg/l (with 95% confidence limits 89.45 – 115.4).
2.Short term toxicity of test material was evaluated for test material Ten neonates less than 24 hr old Daphnids were used for the test . Daphnid stock cultures were fed a mixture of A. falcatus, S. capricornutum, and Chlamydomonas reinhardi 90.
Two replicates were used in each test. Daphnia were gently touched with a pastier pipet at 24 and 48 hr.If the daphnia could not swim actively for 15 s, immobilization (mortality) was recorded. The effective concentrations at which 50% of the organisms are immobilized (EC50) were computed using the probit analysis. The effect concentration of test chemical (EC50) for 50% immobilization of Daphnia magna was observed to be 276.0 mg/l.
On the basis of above effect concentration it can be considered that the test material has no toxic effect on aquatic invertebrates and cannot be classified as per CLP criteria.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 276 mg/L
Additional information
Short term toxicity to aquatic invertebrate:
Data available for the structurally and functionally similar read across chemicals has been reviewed to determine the short term toxicity of aquatic invertebrate of the test chemical (+)-Neomenthol (2216 -52 -6).The studies are as mentioned below:
1. The short term toxicity study of test material was evaluated for aquatic invertebrate Biomphalaria alexandrina snails .
The snails were collected from fresh water ponds (untreated with molluscicides). Specimens were acclimated to laboratory conditions in a glass aquarium containing 5 l of dechlorinated tap water, fed on dry lettuce leaves and oxygenated for 1 h daily, for 1 week prior to experimentation.The median lethal effect concentration (LC50) for 24 h was observed to be 101.59 mg/l (with 95% confidence limits 89.45 – 115.4).
2.Short term toxicity of test material was evaluated for test material Ten neonates less than 24 hr old Daphnids were used for the test . Daphnid stock cultures were fed a mixture of A. falcatus, S. capricornutum, and Chlamydomonas reinhardi 90.
Two replicates were used in each test. Daphnia were gently touched with a pastier pipet at 24 and 48 hr.If the daphnia could not swim actively for 15 s, immobilization (mortality) was recorded. The effective concentrations at which 50% of the organisms are immobilized (EC50) were computed using the probit analysis. The effect concentration of test chemical (EC50) for 50% immobilization of Daphnia magna was observed to be 276.0 mg/l.
On the basis of above effect concentration it can be considered that the test material has no toxic effect on aquatic invertebrates and cannot be classified as per CLP criteria.
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