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EC number: 222-695-1 | CAS number: 3576-88-3
- 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 soil microorganisms
Administrative data
- Endpoint:
- toxicity to soil microorganisms
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
Data source
Materials and methods
Test material
- Reference substance name:
- melam
- IUPAC Name:
- melam
Constituent 1
Results and discussion
Applicant's summary and conclusion
- Executive summary:
# Melam has a low solubility in water and no relevant bioaccumulation potential.
Melam has no toxic effects up to high (limit) concentrations to aquatic microorganisms (see section 6.1.7.) as well as to soil macroorganisms (6.3.1.) and to terrestrial plants (6.1.6.):
- Aquatic microorganisms: The EC50 of the test substance on activated sludge respiration is above 100 mg/L.
- Earthworm: The 7d LC50 and 14d LC50 of the test substance are higher than 100 mg/kg.
- Plants: LC50 (for seedling emergence), EC50 (for growth) and LOEC values are all above 100 mg/kg, NOEC values are all 100 mg/kg.
It can therefore be expected that also the possible acute toxicity of melam to soil microorganisms will be low.
# According to Column 2 of Section 9.4. in the Annex IX of REACH "In the absence of toxicity data for soil organisms, the equilibrium partitioning method may be applied to assess the hazard to soil organisms". This can be applied as toxicity data for aquatic organisms are available. A PNECsoil could be calculated from the PNECwater using Equilibrium Partitioning.
# And further in Column 2: "The choice of the appropriate tests depends on the outcome of the chemical safety assessment." Melam is neither classified nor is it a PBT or a vPvB substance. The chemical safety assessment CSA therefore does not need to include a risk assessment and therefore no "appropriate tests" have to be chosen.
Further tests:
# According to Column 2 of Section 9.4. in the Annex X of REACH "Long-term toxicity testing shall be proposed by the registrant if the results of the chemical safety assessment according to Annex I indicates the need to investigate further the effects of the substance and/or degradation products on terrestrial organisms. The choice of the appropriate test(s) depends on the outcome of the chemical safety assessment."
Melam is neither classified nor is it a PBT or a vPvB substance. The chemical safety assessment CSA therefore does not need to include a risk assessment and therefore does not "indicate the need to investigate further the effects of the substance and/or degradation products on terrestrial organisms."
# According to Column 2 of Section 9.4. in the Annex X of REACH "These studies do not need to be conducted if direct and indirect exposure of the soil compartment is unlikely." A direct exposure of soil is not intended and an indirect exposure to soil is unlikely, as the only use of melam is, to be included into a plastic matrix.
It is concluded that the results of further investigations on the toxicity of melam are not essential for classification or for the chemical safety assessment. A toxicity test with soil microorganisms can be waived.
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