Registration Dossier
Registration Dossier
Diss Factsheets
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EC number: 212-661-4 | CAS number: 840-65-3
- 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

PBT assessment
Administrative data
PBT assessment: overall result
- PBT status:
- the substance is not PBT / vPvB
- Justification:
Persistence:
In an OECD TG 301C study, conducted according to GLP, the degradation of NDC reached 6% (as BOD) and 7% (by HPLC) after 28 and 20, respectively. NDC is not readily biodegradable (Ministry of International Trade and Industry (MITI), 1999). In an OECD 111 study, conducted to GLP, the half life of NDC is 65.9 and 1.04 days in pH 7 and 9, respectively, at 25C. NDC is stable at pH 4 (Ministry of International Trade and Industry, 1996). According to ECHA Guidance Chapter R11 – PBT Assessment, Table R.11-2 Screening criteria for P, vP, B, vB and T, a substance fulfills the screening criteria for Persistence (P) if it does not ultimately biodegrade. NDC, therefore, is considered as Persistent (P) based upon the screening criteria. In addition, according to 1.1.2 of Annex XIII of Regulation EC No 1907/2006, a substance fulfills the very Persistent criterion (vP) when the half life in marine, fresh or estuarine water is >60 days. NDC, therefore, is considered very Persistent (vP) based upon the Annex XIII criteria.
Bioaccumulation:
According to ECHA Guidance Chapter R11 – PBT Assessment, Table R.11-2 Screening criteria for P, vP, B, vB and T, a substance fulfills the screening criteria for bioaccumulation (B) when the Log Pow is >4.5. In an OECD 107 study, conducted according to GLP, the Log Pow of NDC is 3.5 (Ministry of International Trade and Industry (MITI), 1999). NDC, therefore, is not bioaccumulative (B) based upon the screening criteria.
In an OECD 305C study, conducted according to GLP, the BCF of NDC is 6.1 - 63 at a test concentration of 0.1 mg/l. At a test concentration of 0.01 mg/l, the BCF of NDC is 7.1 - 23 (Ministry of International Trade and Industry (MITI), 1999). According to 1.1.2 of Annex XIII of Regulation EC No 1907/2006, a substance fulfills the bioaccumulation criterion (B) when the BCF in aquatic species is higher than 2,000. NDC, therefore, is not bioaccumulative (B) based upon the Annex XIII criteria.
Toxicity:
Based on a NOEL of greater than 1,000 mg/kg bw/day, in accordance with Regulation No 1272/2008, NDC is not classified for reproductive toxicity.
In accordance with Regulation No 1272/2008 Table 3.9.3, NDC is not classified for repeated dose toxicity (oral), based on the NOEL (male and female rats) of >3,000 mg/kg diet (highest dose tested).
Based on the above, NDC is not Toxic (T) in accordance with 1.1.3 of Annex XIII of Regulation EC No 1907/2006.
- Likely routes of exposure:
The primary route of NDC release is to wastewater.
NDC may be released to air through use processes; however, the vapour pressure is 0.00033 Pa at 25 ºC and, therefore, air exposure is expected to be negligible.
Release to soil may occur from spreading of STP sludge, however this is not advised.
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