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EC number: 931-227-1 | CAS number: 28497-59-8
- 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
Short-term toxicity to fish
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to fish
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 1999-12-06 - 1999-12-10
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 203 (Fish, Acute Toxicity Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.1 (Acute Toxicity for Fish)
- Deviations:
- no
- GLP compliance:
- no
- Specific details on test material used for the study:
- Gylcerol: 1,3 dimethacrylate
Batch No: 790703330
Lot: No. 32079289
Reactive ester content: 96.9 %
Diester content: 90.5 %
Triester content: 1.5 %
Inhibitor: 202 ppm HQME
Methacrylic acid: 0.2 % - Analytical monitoring:
- yes
- Details on sampling:
- - Concentrations: 10.7, 18.8. 32.7, 57.1 and 100 mg/l
- Vehicle:
- no
- Details on test solutions:
- - The individual test concentrations were prepared by dilution of stock solution
- Test organisms (species):
- Poecilia reticulata
- Details on test organisms:
- Test organism: Poecilia reticulata (Guppy)
- 7 fish per test convcentration (length of 1-3 cm)
Breeding: Parental and young fish population was held in two 250 I glass aquaria
Illumination: 14 h a day
Temperature: 23 ± 2 °C
Medium: Continuously aerated and filtered tap water from Schlieren. The bottom of the aquaria was covered with gravel (51.5 em). Every month, one
third of the total volume of the aquaria was replaced by fresh tap water.
Feed: Sera micropan, Sera vipan (Sera apanristic GmbH, D-52525 Heinsberg, Germany) daily.
The fish were last fed 24 h before the start of the definitive test.
Measurements: pH, conductivity, oxygen concentration and hardness of water were determined once a week.
Temperature was controlled by a thermostatic heating element. - Test type:
- semi-static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 96 h
- Hardness:
- 17.7 (minimum) - 31.9 (maximum) °F total hardness
- Test temperature:
- 21 ± 1 °C
- pH:
- 8.3 - 8.7
- Dissolved oxygen:
- 0.76 - 8.4 mg oxygen/l
- Nominal and measured concentrations:
- 10.7, 18.8. 32.7, 57.1 and 100 mg/l (nominal)
Reactive test concentrations after 24 h of incubation: 94-98 % - Details on test conditions:
- Medium: Continuously aerated and filtered tap water from Schlieren. The bottom of the aquaria was covered with gravel (51.5 em). Every month, one
third of the total volume of the aquaria was replaced by fresh tap water.
Feed: Sera micropan, Sera vipan (Sera apanristic GmbH, D-52525 Heinsberg, Germany) daily.
The fish were last fed 24 h before the start of the definitive test.
Measurements: pH, conductivity, oxygen concentration and hardness of water were determined once a week.
Temperature was controlled by a thermostatic heating element. - Reference substance (positive control):
- no
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 43.2 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Duration:
- 96 h
- Dose descriptor:
- LC100
- Effect conc.:
- 57.1 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Duration:
- 96 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 32.7 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality (fish)
- Sublethal observations / clinical signs:
Nominal concentration
(mg/l)
Cumulative mortality observed at different points in time
after start of exposure
2h
24h
48h
72h
96h
control
0
0
0
0
0
0
10.7
0
0
0
0
0
18.7
0
0
0
0
0
32.7
0
0
0
0
0
57.1
0
0
3
4
7
100
0
7
a)
a)
-a)
- Validity criteria fulfilled:
- yes
- Remarks:
- During 7 days before the definitive test, mortality in the batch of which fish were used for the test was less than 5 %.
- Conclusions:
- LC50 fish (96h): 43.2 mg/l
- Executive summary:
The acute lethal toxicity (LC50) of GLYCEROL-1 ,3-DIMETHACRYLATE to Poecilia reticulata (Guppy) was investigated under semi-static exposure conditions over a period of 96 h acc. OECD 203 (fish acte toxicity test adopted 1992).
The test medium was replaced every 24 h. 7 fish per concentration were exposed to the test substance.
Nominal concentrations of GLYCEROL-1,3-DIMETHACRYLATE as selected after a preceding limit test were 10.7, 18.7, 32.7, 57.1 and 100 mg/1, respectively.
The individual test concentrations were prepared by dilution of a stock solution. HPLC analyses of the test substance concentration were conducted at the beginning and at the end of every 24 h cycle.
The analyses revealed that the test substance concentrations were satisfactorily maintained over the whole incubation time of 96 h.
In the definitive test all fish died at the nominal concentrations of 100 mg/1 after 24 h of exposure. After 96h all fish were dead at the nominal concentrations of 57.1 mg/1. No mortality was observed at all other test concentrations and in the control after 96 h of exposure. Other toxic effects than mortality, e.g. loss of coordination, hypoactivity and swimming on the back, were not observe
LC50 (96h): 43.2 mg/1 (based on nominal conentrations)
NOEC (96h): 32.7 mg/1.
LC100 (96h): 57.1 mg/1.
Reference
Description of key information
The acute lethal toxicity (LC50) of GLYCEROL-1 ,3-DIMETHACRYLATE to Poecilia reticulata (Guppy) was investigated under semi-static exposure conditions over a period of 96 h acc. OECD 203
Result: LC50 (96h): 43.2 mg/1 (based on nominal concentrations).
Key value for chemical safety assessment
Fresh water fish
Fresh water fish
- Effect concentration:
- 43.2 mg/L
Additional information
Aquatic toxicity of Glycerol 1,3-dimethacrylate is based on narcosis which correlates with log Kow. Log Kow values of substances containing ether groups are known to differ from measured values which means for Glycerol 1,3 dimethacrylate that the calculated log Kow value is lower than measured value. (see Schüürmann G (1990) QSAR Analysis of the acute toxicity of oxyethylated surfactants,
Chemosphere, Vol.21, Nos.4-5, oo 467-47 8 , 1990, Printed in Creat Britain).
The measured log Kow is 2.05. QSAR predictions with OECD toolbox version 3.3 are performed KOWWIN 1.68 which calculates a log Kow of 1.16.
The QSAR prediction of acute fish toxicity was performed to demonstrate on the one hand that the predicted LC50 of 133 mg/l is higher than the measured but primarily that the experimental LC50 fish of 43.2 mg/l correlates with the measured log Kow. Based on this correlation in a further step QSAR predictions for daphnia magna and algae were performed (see 6.1.3 and 6.1.5) and the corrected EC50 values were graphically read for the measured logKow.
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