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Diss Factsheets
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EC number: 200-838-9 | CAS number: 75-09-2
- 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
Ecotoxicological Summary
Administrative data
Hazard for aquatic organisms
Freshwater
- Hazard assessment conclusion:
- PNEC aqua (freshwater)
- PNEC value:
- 0.31 mg/L
- Assessment factor:
- 20
- Extrapolation method:
- assessment factor
- PNEC freshwater (intermittent releases):
- 0.27 mg/L
Marine water
- Hazard assessment conclusion:
- PNEC aqua (marine water)
- PNEC value:
- 0.031 mg/L
- Assessment factor:
- 200
- Extrapolation method:
- assessment factor
- PNEC marine water (intermittent releases):
- 0.027 mg/L
STP
- Hazard assessment conclusion:
- PNEC STP
- PNEC value:
- 26 mg/L
- Assessment factor:
- 100
- Extrapolation method:
- assessment factor
Sediment (freshwater)
- Hazard assessment conclusion:
- PNEC sediment (freshwater)
- PNEC value:
- 2.57 mg/kg sediment dw
- Extrapolation method:
- equilibrium partitioning method
Sediment (marine water)
- Hazard assessment conclusion:
- PNEC sediment (marine water)
- PNEC value:
- 0.26 mg/kg sediment dw
- Extrapolation method:
- equilibrium partitioning method
Hazard for air
Air
- Hazard assessment conclusion:
- no hazard identified
Hazard for terrestrial organisms
Soil
- Hazard assessment conclusion:
- PNEC soil
- PNEC value:
- 0.33 mg/kg soil dw
- Extrapolation method:
- equilibrium partitioning method
Hazard for predators
Secondary poisoning
- Hazard assessment conclusion:
- no potential for bioaccumulation
Additional information
For DCM short term L(E)C50 values from validated sources are reported for fish and invertebrates. For fresh water fish the lowest LC50 value from validated data is 97 mg/l (Fundulus heteroclitus), for invertebrates the lowest LC50 value is 27 mg/l (Daphnia magna).
In addition to short-term toxicity data, long- term toxicity data are reported for fish and algae, but only a modeled 21d NOEC range for daphnids between 6.2 -13.3 mg/L. For fish a 28-day NOEC value of 83 mg/l is reported for Pimephales promelas. For fresh water algae an 8-day Toxicity Threshold value, equivalent to an EC3 value, of 550 mg/l is reported, which can be considered a long-term NOEC value. These chronic data have been used to derive the PNECs, but as a modeled value was included, an additional AF of 2 was used on the lowest chronic value available (6.2 mg/L for daphnids).
The toxicity of dichloromethane to activated sludge was evaluated by a simple respirometric procedure set up on the basis of OECD Method 209. The exposure duration, however, was only 40 minutes. Several other studies were available; however these studies were either less relevant for toxicity towards STP-organisms or the toxicity values were indecisive (greater than values). The lowest threshold level (40-min EC50) was 2590 mg/l in aerobic domestic sludge.
No reliable data is available for sediment or soil organisms. Various studies were performed with Eisenia fetida (earthworm) and various higher plants. However, they were either not relevant for the endpoint or the original study could not be found and the available information was not sufficient.
Conclusion on classification
DCM has a harmonized classification (Index no. 602 -004 -00 -3). DCM does not have a harmonized classificication for environment (neither acute nor chronic).
Three acute endpoints for three different trophic levels are available. The lowest EC50 is found for Daphnia magna and is 27 mg/L.
Results of validated structure activity relationships and expert judgment may be taken into account where appropriate with regard to classification and labelling of substances. Long-term study results are also available:
a 28-d NOEC of 83 mg/L for Pimephales promelas; EC3 of 550 mg/L for the alga species Microcystis and a modeled value for daphnids, a 21d NOEC of 6.2 -13.3 mg/L.
The substance is readily biodegradability and has a low log Kow of 1.25.
Acute endpoints are all > 1 mg/L, therefore under Regulation (EU) No 286/2011 (2nd ATP to CLP) DCM does not need to be classified acute aquatic hazardous.
The substance is readily biodegradable and all chronic endpoints are > 1.0 mg/L. Therefore, DCM does not need to be classified chronic aquatic hazardous.
Proposal for self-classification: Not classified for environment
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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