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Diss Factsheets
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EC number: 239-556-6 | CAS number: 15520-10-2
- 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
Endpoint summary
Administrative data
Description of key information
For a summary on available key information, please see below.
Additional information
Because of the short carbon chain length of MPMD, any surface-active properties can safely be excluded. Due to the high primary and secondary pKa-values, MPMD will be present in the aqueous environment exclusively as a di-cation. This results firstly in a negligible volatility from water; and secondly, partitioning between n-octanol and water is exclusively into the water phase, leading to a very low Kow (log Kow <1) and excluding any partitioning based bioaccumulation. At the same time, two positive charges separated by only a short C5-spacer implies a very low (if any - for details see read-across report in IUCLID section 13) potential to cross biological membranes. Accordingly, there is no potential for bioaccumulation, and thus secondary poisoning is no issue for MPMD. Aliphatic amines are readily protonated at environmental pH and due to their positive charge are prone to bind to negatively charged solid matter. According to the available adsorption-desorption study (OECD 106; RL1) on read across source substance 1,6-hexane diamine (HMD), there is relevant binding to soil and sediment. In spite of this adsorptive behaviour, MPMD was shown to be readily biodegradable fulfilling the 10-day window requirement with total nitrification within 28 days (measured nitrate concentration approximately equalled the theoretical one). From these properties, rapid degradation in sewage treatment plants or the environment is expected which would lead to overall low environmental concentrations. In addition, due to adsorption on suspended matter or soil, bioavailable concentrations in the aquatic phase are expected to be low. Due to the observed rapid mineralization, accumulation in soil or sediment is not anticipated. This is confirmed by the study on nitrogen-transformation of read-across source substance HMD by soil organisms (OECD 216; RL 1): independently from the substance concentration (between 62.5 and 1000 mg/kg soil dry weight), consistently between 50% and 64% of the substance borne nitrogen was transformed to nitrate within 28 days, in addition to the nitrate stemming from amending soil with Lucerne meal containing nitrogen. As cleavage of the C-N-bonds is a prerequisite for nitrification and will reduce adsorption and increase bioavailability; and considering in addition ready biodegradability; this allows for concluding on rapid mineralization of MPMD within natural soil.
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