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EC number: 221-641-4 | CAS number: 3173-72-6
- 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:
- 0.009 mg/L
- Assessment factor:
- 1 000
- Extrapolation method:
- assessment factor
- PNEC freshwater (intermittent releases):
- 0.087 mg/L
Marine water
- Hazard assessment conclusion:
- PNEC aqua (marine water)
- PNEC value:
- 0.001 mg/L
- Assessment factor:
- 10 000
- Extrapolation method:
- assessment factor
STP
- Hazard assessment conclusion:
- PNEC STP
- PNEC value:
- 100 mg/L
- Assessment factor:
- 100
- Extrapolation method:
- assessment factor
Sediment (freshwater)
- Hazard assessment conclusion:
- PNEC sediment (freshwater)
- PNEC value:
- 0.015 mg/kg sediment dw
- Extrapolation method:
- equilibrium partitioning method
Sediment (marine water)
- Hazard assessment conclusion:
- PNEC sediment (marine water)
- PNEC value:
- 0.001 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:
- 0.001 mg/kg soil dw
- Extrapolation method:
- equilibrium partitioning method
Hazard for predators
Secondary poisoning
- Hazard assessment conclusion:
- no potential for bioaccumulation
Additional information
- CLP [(EU) No 286/2011 "... The NOECs or other equivalent ECx (e.g. EC10) shall be used."
- Guidance on information requirements and chemical safety assessment, Chapter R.10: Characterisation of dose [concentration]-response for environment: " An EC10 for a long-term test which is obtained using an appropriate statistical method (usually regression analysis)will be used preferentially."
- OECD 201 "Recent scientific developments have led to a recommendation ofabandoning the concept of NOEC and replacing it with regression based point estimates ECx.")
Lowest effect values reported in ecotox studies are as follows:
Fish: LL0 >50 mg/L (Bayer Industry Services 2005a)
Daphnia: EL0 >100 mg/L (Bayer Industry Services 2005b)
Algae: ErC50 8.744 mg/L, ErC10 0.512 mg/L, NOECr0.073 mg/L (Bayer Industry Services 2006)
Considering the NOECrof 0.073 mg/L and the fact, that the substance is rapidly degradable (hydrolysis half time <1 hour), a classification of chronic cat. 2 (H411) according to Regulation EC No. 1272/2008 would be required. The reported NOEC value is indeed statistically significant, but not from a biological point of view. The reported ErC10 of 0.512 mg/L is statistically and biologially valid. Based on this result, and as the substance is rapidly degradable, a classification chronic cat. 3 (H412) is required according to Regulation EC No. 1272/2008.
The concept of using the EC10 instead of a NOEC is discussed in relevant documents as presented in the following
Conclusion on classification
The classification of 1,5-naphthylene diisocyanate was based on the parent substance. Rapid hydrolysis of the substance was determined in an OECD 11 study on hydrolytical behaviour. While the formation of the reaction product 1,5 -naphthylene diamine was reported in this study it was demonstrated that this should be understood as the consequence of artificial test item preparation conditions (i.e. stirring). Under environmentally relevant conditions the final reaction product should be chemically inert poly-urea (for details see discussion in "hydrolysis" endpoint summary). The classification of 1,5 -naphthylene diisocyanate should, thus, be based on either poly-urea which is not classified according to Regulation (EC) No 1272/2008 or on the parent substance itself and the latter one was found to be appropriate.
Classification of 1,5-naphthylene diisocyanate based on Regulation (EC) No 1272/2008
- Category acute: There is only one acute category with the criterion: L/EC50 <= 1 mg/L. For 1,5-naphthylene diisocyanate there are studies on acute toxicity for fish, daphnids and algae and the lowest L/EC50 was reported as 8.74 mg/L (algae).
Result: The lowest L/EC50 was clearly higher than the criterion and, thus, there is no justification for a classification based on acute toxicity of 1,5-naphthylene diisocyanate.
- Category chronic: There are data on short-term toxicity (fish, daphnids, algae) as well as chronic data (algae). With this dataset the classification has to be decided based on both acute and chronic data and the more critical classification has to be used for classification.
a) Classification based on chronic data:
- Rapid degradation? Yes, due to rapid hydrolysis
- Lowest NOEC/EC10? Is in the range of 0.1-1 mg/L (= 0.512 mg/L for algae)
=> Result: Classification “category chronic 3” based on chronic data
b) Classification based on acute data:
- Lowest L/EC50? Is in the range 1-10 mg/L (= 8.74 mg/L for algae)
- BCF >= 500? No, the experimental BCF is < 4.5
- Log Kow >= 4? No, the experimental log Kow is 0.91
=> Result: No chronic classification based on acute data
Conclusion, 1,5-naphthylene diisocyanate does not need to be classified for acute toxicity but for chronic toxicity “category chronic 3” is justified (H412).
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