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Diss Factsheets
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EC number: 201-234-8 | CAS number: 79-92-5
- 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)
Description of key information
EC50 aquatic invertebrates: 0.72 mg/L
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 0.72 mg/L
Additional information
In the GLP compliant Klimisch 1 study from Ágh (2012), the acute toxicity of Camphene, technical grade, solid to Daphnia magna was determined according to OECD 202 and EU method C.2 in a semi-static test (24 hour renewal interval) . The test item has a purity of 82.6 % by weight and contains 12.4 % Tricyclene as impurity. A supersaturated solution (nominal loading: 1000 mg/L) was first prepared by mixing an excess of the test item in dilution water (Elendt M4 medium). This mixture was shaken overnight and then the non-dissolved test material was separated to give the stock solution at the limit of solubility level in the test medium. This stock solution was further diluted with dilution water to result in following dilutions:26.0, 36.4, 51.0, 71.4 and 100 % v/v saturated solution. Due to immobilization at 24 hours in the lowest test concentration, further dilutions with 13.3 and 18.6% were set up (experiment 2). The concentration of Camphene was experimentally determined. and following geometric mean measured concentrations were obtained: Experiment I: 0.83, 1.12, 1.35, 2.10 and 3.29 mg/L and Experiment II: 0.48 and 0.73 mg/L. After 48 hours, 0,0, 55, 80, 100, 100, 100 and 100% immobilisation was observed in the control and at mean measured 0.48, 0.73, 0.83, 1.12, 1.35, 2.10 and 3.29 mg/L. During the 24 hour aging period of the solutions the concentration of the test item declined to about 1/3 of the initial concentrations. Therefore, the concentrations were based on mean measured concentrations. The NOEC was 0.48 mg/L, the EC50 was calculated to be 0.72 mg/L.
The results of this study are considered relevant and reliable for the risk assessment.
In the Klimisch 3 study from LeBlanc (1980) the acute toxicity of camphene was determined on Daphnia magna using a static test design. The daphnia were exposed to several concentrations of test substance for 48 hours at 22±1 ºC. Test method according to US EPA (1975): Methods for acute toxicity tests with fish, macro invertebrates and amphibiens. After 48 hours, the EC50 was 22 (13 - 36) mg/L (basis for effect: mortality). Since no dose verification was performed, the test is was classified as Klimisch 3 study. The results from this study will not be taken for the risk assessment.
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