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EC number: 221-375-9 | CAS number: 3081-14-9
- 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
Biodegradation in soil
Administrative data
Link to relevant study record(s)
Description of key information
Read-across was performed using data from a similar paraphenylediamine 7PPD (N-(1,4-dimethylpentyl)-N'-phenylbenzene-1,4-diamine) . A read-across justification using structural considerations, relevant PC-data (water solubility, logKow), fate data (biodegradation, logKoc) as well as ecotoxicological data is attached in IUCLID chapter 13.
Aerobic conditions: The metabolism of 14C-7PPD in aerobic soils is proposed to proceed via formation of minor transient metabolites and mineralization. The main portion of the residue is binding to the soil matrix and appears to become unavailable for further degradation/mineralization. DT50 values of the parent, derived from FOMC (First-Order Multi Compartment kinetics), were 1.4 – 1.9 days for Soils II-IV and < 1 day for soil I.
Anaerobic conditions: The rapid decline of 7PPD in the initial aerobic phase was likely to extend into the anaerobic phase of the test system given, that the transition to anaerobic conditions by soil flooding is progressive. Therefore, the short DT50 of 7PPD (1.5 days) in the flooded test system was attributed to aerobic degradation. Following that rapid initial decline, the parent dissipated slowly, from 23.2% AR on day 1 to 17.0 AR on day 120.
Key value for chemical safety assessment
- Half-life in soil:
- 1.9 d
- at the temperature of:
- 12 °C
Additional information
Aerobic conditions:
DT50 values derived from First Order Multi Compartment kinetics (FOMC) kinetics were 1.4 – 1.9 days for Soils II-IV and < 1 day for soil I. The faster decline in acid soil I (pH 3.8) was explained by the instability of 7PPD under acidic conditions.
The metabolism of 14C-7PPD in aerobic soils is proposed to proceed via formation of minor transient metabolites and mineralization.The main portion of the residue is binding to the soil matrix and appears to become unavailable for further degradation/mineralization.
Anaerobic conditions:
The short DT50 of the parent (1.5 days) in the flooded test system was attributed to aerobic degradation. Following that rapid initial decline, 7PPD dissipated slowly. A DT90 of >1000 days was calculated. The metabolite 1-N-(5-methyl-hexan-2-yl)-4-N-phenylcyclohexa-2,5-dione-4,4-diimine also known as 7QDI, (cis/trans isomers) was observed.
7QDI Isomer 1: DT50 = 57.9 d; DT90 = 192 d
7QDI Isomer 2: DT50 = 79.7 d; DT90 = 265 d
7QDI Isomer 1+2: DT50 = 66.9 d; DT90 = 222 d
Degradation was described by SFO (Single First Order) model.
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