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EC number: 700-487-6 | CAS number: -
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
For the assessment of aquatic toxicity of Epoxy half acrylate short-term toxicity data with fish, aquatic invertebrates, algae and microorganisms are available.
Short term toxicity to fish
In a 96 h acute toxicity study according to OECD guideline 203, adopted 17 July 1992, Zebrafish (Danio rerio) were exposed to Epoxy half acrylate
(100% a.i.) at nominal concentrations of 0, 0.625, 1.25, 2.50, 5.00 and 10.0 mg/L, corresponding to geometric mean weighted loading levels of 0, 0.239, 0.599, 1.25, 3.27 and 4.98 mg/L under semi-static conditions with daily renewal. 7 test organisms were exposed to each loading level and the control.The concentrations of the analytes of the test item were analytically verified by LC-MS/MS from freshly prepared test media after 0 and 72 hours and corresponding 24 h aged test media after 24 and 96 hours of all concentration levels and the control.
Effect levels are given based on overall geometric mean weighted test item loadings.
100% mortality was observed at 4.98 mg/L. Sublethal effects (hyperventilation and missing escape reflex) were observed at a concentration of 3.27 mg/L. No mortality or sublethal effects were present at up to 1.25 mg/L.
The 96 h LC50 was 2.02 mg/L (95% CL: 1.25-3.27 mg/L).
Short term toxicity to aquatic invertebtates
The 48 hr acute toxicity of Epoxy half acrylate to Daphnia magna was studied under static conditions. Daphnids were exposed to control and test chemical at nominal concentrations of 0 (control), 10, 18, 32, 56 and 100 mg/L, corresponding to measured concentrations of 0, 6.4, 5.92, 5.48, 6.94 and 4.57 mg/L. Due to the low water solubility the correlation between nominal and measured concentration was very poor. At the end of the test the measured values were higher than at the beginning of the test (except of the treatment 32 mg/L). This was probably caused by dissolved excrements of the daphnia as it can be seen in the control. Therefore, the nominal concentrations were used for the determination of the biological results.
Mortality/immobilisation and sublethal effects were observed daily. Two concentrations showed toxicity between 0 and 100% immobilisation. None of the animals were immobilised in the control.
The 24 h-EC50 of potassium dichromate was tested in a current positive control test. The value was determined as 1.1 mg/L, lying within the demanded range of 0.6 – 1.7 mg/L.
The 48 hour EC50 of Epoxy half acrylate was determined to be 55 mg/L (nominal).
Toxicity to aquatic algae and cyanobacteria
In a 72 hour acute toxicity study, the cultures of Desmodesmus subspicatus, strain CHODAT were exposed to Epoxy half acrylate at nominal concentrations of 0 (control), 1, 2.2, 4.6, 10, 22, 46, 100 mg/L under static conditions in accordance with OECD guideline 201. As the test item is poorly soluble in water, the water-accommodated fraction was tested. This was done by shaking the nominal load with the appropriate amount of deionised water for 24 hours, followed by membrane filtration.
At the beginning and at the end of the test, the content of test item was determined by DOC-determination in the test solutions. The content of the test item was calculated from the DOC measurement. Due to the low water solubility the correlation between nominal and measured concentration was very poor. Therefore, the nominal concentrations were used for the determination of the biological results.
The 72 h NOEC and 72 h EC50 based on growth rate were 4.6 and 315 mg/L. The 72 h NOEC and 72 h EC50 based on yield were 4.6 and 8 mg/L.
Toxicity to microorganisms
In a 3 h respiration inhibition study, activated sludge a predominantly municipal sewage treatment plant was exposed to Epoxy half acrylate at nominal concentrations of 0 (control), 10, 32, 100, 320 and 1000 mg/L in accordance with OECD Guideline 209 (2010). Copper (II) sulphate pentahydrate at concentrations of58, 100 and 180 mg/L was used as reference substance. The respiration rates of the control, reference and test item replicates were measured after a contact time of three hours, and the inhibitory effects of the test and reference item were determined in comparison to the control respiration rates. The mean inhibition of respiration for the test item replicates ranged from 3%to 63%.
The 3 h EC50 of Epoxy half acrylate was determined to be 594 mg/L, the 3 h EC10 was 31.7 mg/L, the 3 h NOEC was 10 mg/L.
The most sensitive organism to Epoxy half acrylate was Danio rerio. Thus, the lowest acute toxicity value is the 96 h LC50 to Danio rerio of 2.02 mg/L. This value is used for the calculation of PNECs.
Based on these results and the substance being not rapidly biodegradable, Epoxy half acrylate has to be classified as Aquatic Chronic 2.
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