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Diss Factsheets
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EC number: 203-714-2 | CAS number: 109-87-5
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
Description of key information
The pieces of information that build the weight of evidence are the following:
A) in vivo study from Burlion N & Galloy A (1991)
Purity of min. 99.9%
Mehod not fully described
EC50 (5d): 6000 mg/L
B) QSAR for acute prediction from Pavan M (2015)
Fully documented with QPRF and QMRF
EC50 (96h): 874.12 mg/L
C) QSAR for chronic prediction from Pavan M (2012)
Fully documented with QPRF and QMRF
NOEC (30d): 145.770 mg/L
D) Read-across for acute toxicity from Pavan M (2015)
Analogue approach justified with data matrix (source chemical: dimethoxyethane)
EC50 (72h): 9120 mg/L
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 874.12 mg/L
- EC10 or NOEC for freshwater algae:
- 145.77 mg/L
Additional information
The weight of evidence approach is justified as determined from more than one piece of information (independent sources). We claim the reliability, relevance, adequacy and quality of the weight of evidence:
- Reliability: Klimisch score of 2 is assigned to the pieces of information.
- Relevance:
o Relevance of test material: substance purity is >99.9% in the laboratory test. The test material is equivalent to the submission substance identity. Relevance for QSAR is defined in QPRF and QMRF. The target Dimethoxymethane and the source 1,2-dimethoxyethane can be considered sufficiently structurally and mechanistically similar to apply the read-across approach. Relevance of the read-across approach is supported by structural similarity between the source and the target chemicals and is also supported by a close similarity in terms of mechanism of action, physicochemical and reactivity properties relevant for acute aquatic toxicity on algae.
o Relevance of test method and conditions: whereas deficiencies are noted in laboratory test, the tested method follows, broadly speaking, the internationally approved test guidelines. Relevance for QSAR is defined in QPRF and QMRF. Relevance of the read-across is supported by the key study status of the source study.
o Relevance of the endpoint: the values obtained extend over 3 different approaches and show a clear evidence of low aquatic toxicity to algae:
-> In vivo test: EC50(5d): 6000 mg/L
-> QSAR prediction: EC50(96h): 874.12 mg/L and NOEC: 145.77 mg/L
-> Read-across prediction: EC50(72h): 9120 mg/L
o Relevance of alternative methods: relevance of QSAR is defined in QPRF and QMRF. Relevance of the read-across is supported by the clear analogy between the source and the target chemicals.
- Adequacy: the clear trend resulting from 3 different approaches allow a clear decision related to classification: the endpoint are higher than the cut-off values for classification as acute or chronic aquatic hazard.
- Quantity: four pieces of information are considered.
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.
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