Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 200-579-1 | CAS number: 64-18-6
- 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

Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
Description of key information
Key value for chemical safety assessment
- EC10 or NOEC for microorganisms:
- 72 mg/L
Additional information
As key study regarding toxicity to microorganisms, an inhibition control of a test on ready biodegradability according to EU method C.3 was identified, using domestic activated sludge as inoculum. Within the test period of 13 days, no inhibition of degradation activity could be observed. Hence, the test substance concentration of 72 mg/L is considered to be a NOEC, used for PNEC derivation.
Furthermore, three relevant and reliable supporting studies are available. One is a respiration inhibition test with industrial activated sludge following ISO/DIS 8192 Part B (draft 1984) which is similar to OECD TG 209 (BASF AG, 1988). Although performed under non-neutralized conditions, stimulation rather than an inhibition of the respiration activity was measured at a test concentration of 988 mg formic acid/L. Therefore, the EC20 was > 988 mg/L.
The second and third study is a growth inhibition test with Pseudomonas putida following the German Industrial Standard DIN 38412, part 8 (BASF AG, 1991; Trenel et al. 1982). The EC50was determined to be 46.7 mg formic acid/L in the test performed by BASF while Trenel et al. found an EC10 of 3160 mg/L. Besides the fact that the result of the BASF study is driven by the acidity of non-neutralized formic acid and that the documentation of the study of Trenel et al. does not contain information on pH value while testing , this type of study using Pseudomonas putida is less relevant for this endpoint since glucose was added as substrate (rf. REACh Guidance r10 and TGD, 2003).
As all supporting studies reveal methodological deficiencies (industrial sludge used; pH dependent effect; no details on test performance), the inhibition control of the biodegradability test was chosen to be the key study.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
