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Diss Factsheets
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EC number: 939-707-2 | CAS number: -
- 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
Additional information
The terrestrial toxicity data of Reaction product of naphthalene, butanol, sulfonated and neutralized by caustic soda have been determined by a read-across approach based on analogue substance Reaction product of naphthalene, propan-2-ol, sulfonated and neutralized by caustic soda.
The terrestrial toxicity data of Reaction product of naphthalene, butanol, sulfonated and neutralized by caustic soda are summarized below:
Toxicity to soil macroorganisms:
Sodium diisopropylnaphthalenesulphonate did not reduce the reproduction of Eisenia fetida at a nominal concentration of 6.0 mg a.i./kg d.s. after 56 days of exposure (NOEC). The 56-day EC50 for reproduction exceeded the highest concentration tested, i.e. was above 162 mg a.i./kg d.s.
Based on the results of this study, by analogy (Read across approach) Reaction product of naphthalene, butanol, sulfonated and neutralized by caustic soda has no effect on soil macroorganisms.
Toxicity to soil microorganisms:
Supragil WP (sodium diisopropylnaphthalenesulphonate) tested at 1.00, 10.0, 100, 500 and 1000 mg/kg dry soil, showed a statistically significant effect on soil nitrogen mineralisation compared to the control treatment at 100, 500 and 1000 mg product/kg dry soil on the rate of transformation at the end of the 28 day test period (Dunnett’s two tail, p=0.05). The concentration of nitrate in the soil at the end of the test period was statistically different from the control treatment in all treatements except the lowest at 1.00 mg product/kg. For the Day 0 to 28 period, the EC10 , EC25 and EC50 for the rate of nitrate production (net mineralisation) were estimated at 164, 260 and 420 mg Supragil WP/kg dry soil, respectively. As there is a difference in the rate of nitrate production between the control replicates and the higher treatment rates was greater than 25% from Day 0 to Day 28, Supragil WP can be assessed as having a long-term influence on the nitrogen transformation in soils at concentrations ≥100 mg product/kg dry soil.
Based on the results of this study, by analogy (Read across approach) Reaction product of naphthalene, butanol, sulfonated and neutralized by caustic soda has no effect on soil microorganisms.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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