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EC number: 206-058-5 | CAS number: 298-12-4
- 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:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.2 (Acute Toxicity for Daphnia)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- RCC Ltd - Zelgliweg 1 - 4452 Itingen/Switzerland
- Analytical monitoring:
- yes
- Details on sampling:
- For the determination of the actual test item concentrations, duplicate samples were taken from each treatment befor the start of the test and at the end of the test after 48 hours.
For the 48-hour stability samples, the contents of the respective replicates were combined prior to sampling.
All samples were stored deep-frozen (at about -20 °C) immediately after sampling. - Vehicle:
- yes
- Details on test solutions:
- The test medium of the highest nominal concentration of 200 mg/L was prepared by dissolving 301.7 mg of test item completely in 1500 mL of test water using intense stirring for 15 minutes at room temperature. Adequate volumes of this test medium were diulted with test water to prepare the test media with the lower test item concentrations. The test media were prepared just before introduction of the daphnids (i.e., start of the test).
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- The study was performed with young daphnids of the species Daphnia magna Straus. A clone of this species (defined by the supplier as clone 5) was originally supplied by the University of Sheffield/UK in 1992. Since that time, the clone has been bred in the Laboratories of RCC in reconstitued water of the quality identical to the water quality used in the tests (in respect to pH, main ions, and total hardness) and under temperature and light conditiosn identical to those of the test. A the start of the test, the organisms used in the test were 6-24 hours old and were not first brood progeny.
For evaluation of the quality of the daphnia clone and the experimental conditions, potassium dichromate is tested as a positive control twice a year. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Post exposure observation period:
- 48 h
- Hardness:
- 2.5
- Test temperature:
- 20 °C
- pH:
- The pH of the test medium with the highest test concentration of nominal 200 mg/L was 4.0 after the test item application. The pH was adjusted to 6.2 with 25 drops of a 1 M sodium hydroxide solution.
- Nominal and measured concentrations:
- The following nonimal concentrations of Glyoxylic acid 50 % were tested: 9.3, 20, 43, 93 and 200 mg/L.
Additionally, a control was tested in parallel (test water without test item). Nominal concentrations above 200 mg/L were not tested. - Details on test conditions:
- For each treatment, 20 daphnids were used divided into four replicates of five daphnids each.
The volume of test solution provided for each daphnia was 10 mL. Thus, the requirement of the test guidelines for the minimum volume of 2 mL test medium per daphnia was fulfilled. The daphnids were randomly distributed to the test vessels at initiation of the test.
For further information see section "Any other information on materials and methods incl. tables". - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 200 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Duration:
- 48 h
- Dose descriptor:
- EC0
- Effect conc.:
- 200 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 200 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Duration:
- 48 h
- Dose descriptor:
- EC100
- Effect conc.:
- > 200 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- > 200 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Details on results:
- The analytically determined concentration of the test item in the analyzed test medium (nominal 200 mg/L test item) at the start and the end of the test was 85 and 81 % of the nominal value, respectively. Under the conditions of the test, the test item Glyoxylic acid 50 % was sufficiently stable during the test period of 48 h.
Therefore, all reported results are related to the nominal concentration of the test item Glyoxylic acid 50 % and Glyoxylic acid (concentration in brackets).
In the control and at the test concentrations up to and including the nominal concentration of 200 mg/L (100.3 mg/L), no immobilized test organisms were observed during the test period of 48 hours.
Therefore, the 48-hour NOEC and the 48-hour EC0 to Daphnia magna were determined to be at least 200 (100.3) mg/L.
The 48-hour NOEC and the 48-hour EC0 might even be higher but concentrations above 200 (100.3) mg/L. The 48-hour EC50 and the 48-hour EC100 were clearly hiher than 200 (100.3) mg/L.
These values could not be quantified due to the absence of toxicity at the test concentration up to and including the nominal concentration of 200 (100.3) mg/L.
No remarkable observations were made concerning the appearance of the test media. All test media were clear solutions throughout the entire test duration.
At the beginning and the end of the test period, the dissolved oxygen concentrations in the test media and the control were at least 8.1 mg/L, the pH value of the test medi was in the range of 6.2 to 7.8 (after adjustment) and the water temperature during the test was in the range of 20°C. - Results with reference substance (positive control):
- For evaluation of the quality of the daphnia clone and the experimental conditions, potassium cichromate is tested as a positive control twice a year.
- Results with reference substance valid: yes, (historical range of the RCC laboratory 1996-2007: 48-h EC50 : 0.53-1-1 mg/L)
- EC50/LC50: 0.84 mg/L (last test June 2007) - Validity criteria fulfilled:
- yes
- Conclusions:
- The 48-hour NOEC and the 48-hour EC0 to Daphnia magna were determined to be at least 200 (100.3) mg/L.
The 48-hour EC50 and the 48-hour EC100 were clearly higher than 200 (100.3) mg/L.
These values could not be quantified due to the absence of toxicity at the test concentration up to and including the nominal concentration of 200 (100.3) mg/L - Executive summary:
The acute toxicity of the test item Glyoxylic acid 50 % to Daphnia magna was determined in a 48 -hour static test according to the EU Commission Directive 92/69/EEC, Part C.2 (1992) and the OECD Guideline for Testing of Chemicals, No 202 (2004).
The nominal test item (Glyoxylic acid 50 %) concentrations tested were 9.3, 20, 43, 93 and 200 mg/L. A control group was tested in parallel.
The analytically determined concentration of the test item in the analyzed test medium (nominal 200 mg/L) at the start and the end of the test was 85 and 81 % of the nominal value, respectiveley. Under the conditions of the test, the test item Glyoxylic acid 50 % was sufficiently stable during the test period of 48 hours. Therefore, all reported results are related to the nominal concentration of the test item Glyoxylic acid 50 % and Glyoxylic acid (concentration in brackets).
In the control and at the test concentrations up to and including the nominal concentration of 200 mg/L (100.3 mg/L), no immobilized test organisms were observed during the test period of 48 hours.
Therefore, the 48-hour NOEC and the 48-hour EC0 to Daphnia magna were determined to be at least 200 (100.3) mg/L. The 48-hour NOEC and the 48-hour EC0 might even be higher but concentrations above 200 (100.3) mg/L were not tested. The 48 -hour EC50 and the 48 -hour EC100 were clearly higher than 200 (100.3) mg/L. These values could not be quantified due to the absence of toxicity at the test concentration up to and including the nominal concentration of 200 (100.3) mg/L.
Reference
Description of key information
In the control and at the test concentrations up to and including the nominal concentration of 200 mg/L (100.3 mg/L), no immobilized test organisms were observed during the test period of 48 hours.
Therefore, the 48-hour NOEC and the 48-hour EC0 to Daphnia magna were determined to be at least 200 (100.3) mg/L. The 48-hour NOEC and the 48-hour EC0 might even be higher but concentrations above 200 (100.3) mg/L were not tested. The 48 -hour EC50 and the 48 -hour EC100 were clearly higher than 200 (100.3) mg/L. These values could not be quantified due to the absence of toxicity at the test concentration up to and including the nominal concentration of 200 (100.3) mg/L.
Key value for chemical safety assessment
Additional information
The acute toxicity of the test item Glyoxylic Acid 50 % to Daphnia magna was determined in a 48 -hour static test according to OECD TG 202 (2004) and GLP.
The nominal test item (Glyoxylic Acid 50 %) concentrations tested were 9.3, 20, 43, 93 and 200 mg/L. A control group was tested in parallel.
The analytically determined concentration of the test item in the analyzed test medium (nominal 200 mg/L) at the start and the end of the test was 85 and 81 % of the nominal value, respectiveley. Under the test conditions Glyoxylic Acid 50 % was sufficiently stable during the test period of 48 hours. Therefore, all reported results are related to the nominal concentration of the test item Glyoxylic Acid 50 % and Glyoxylic Acid (concentration in brackets).
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