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EC number: 423-970-0 | CAS number: 182926-43-8 ORANGE DER 8089
- 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
Reactive Orange 136 was not readily biodegradable and half-life period at pH 4 and pH 7 were 12233.9 h (about 1.4 years) and 84.8 h (about 3.5 days) at 25 °C respectivelywhile is unstable at pH 9 with a half-life period of shorter than one day at 25 °C
The bioconcentration factors of test substance were<=0.6 in level 1 and <=5.6 in level 2 for peak 1, and <=4.1 in level 1 and <=40 in level 2 for peaks 1, 2 and 3.
It is regarded as little mobile in soils.
Additional information
Study reports have been available for the ready biodegradability test, inherent biodegradability test, hydrolysis as a function of pH, bioaccumulation test and adsorption / desorption test. The results are summarized as below:
From the results of the ready biodegradability test (degradation: 0 % on day 28) and BOD5/COD ratio (BOD5/COD=1.6 %), it can be concluded the test substance is not readily biodegradable. The inherent biodegradability test was available according to OECD Guideline 302B. The biodegradation of test substance on day 28 was 18 % and was found to be slightly biodegradable over the 28-day exposure period under the test conditions.
Results of hydrolysis as a function of pH study showed half-life period at pH 4 and pH 7 were 12233.9 h (about 1.4 years) and 84.8 h (about 3.5 days) at 25 °C respectively while is unstable at pH 9 with a half-life period of shorter than one day at 25 °C.
In bioaccumulation test, the bioconcentration factors were<=0.6 in level 1 and <=5.6 in level 2 for peak 1, and <=4.1 in level 1 and <=40 in level 2 for peaks 1, 2 and 3.
The adsorption and desorption of FAT 45'176/A were determined in a screening test by the batch equilibrium method using three soils: Speyer (loamy sand), Les Barges (silt loam) and Sisseln (sandy loam) . The result showed the KOC values were 1105 ml/g, 1156 ml/g and 1249 ml/g for soils, Sisseln and Les Barges, respectively. FAT 45'176/A can therefore be regarded as little mobile in soils.
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