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EC number: 235-437-8 | CAS number: 12227-62-2 This substance is identified in the Colour Index by Colour Index Constitution Number, C.I. 16185:1.
- 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
Adsorption / desorption
Administrative data
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption
- Remarks:
- adsorption
- Type of information:
- calculation (if not (Q)SAR)
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- accepted calculation method
- Justification for type of information:
- Estimated data generated using the EPI Suite model developed by the USEPA.
- Qualifier:
- according to guideline
- Guideline:
- other: Modeling database
- Principles of method if other than guideline:
- Prediction done using KOCWIN Program (v2.00)
- GLP compliance:
- not specified
- Type of method:
- other: MCI Method
- Media:
- soil
- Specific details on test material used for the study:
- -Name of test material: Aluminium, 3-hydroxy-4-[(4-sulfo-1-naphthalenyl)azo]-2,7-naphthalenedisulfonic acid complex
- Molecular formula: C20H14AlN2O10S3
- Molecular weight: 565.51 g/mol
- Substance type: Organic
- Physical state: Solid - Radiolabelling:
- not specified
- Test temperature:
- 25 deg.C
- Analytical monitoring:
- not specified
- Key result
- Type:
- Koc
- Value:
- 1 260 000 L/kg
- Temp.:
- 25 °C
- Remarks on result:
- other: Log Koc= 6.1003 (estimated by MCI method)
- Validity criteria fulfilled:
- not specified
- Conclusions:
- The Soil Adsorption Coefficient i.e. Koc value of test chemical Aluminium, 3-hydroxy-4-[(4-sulfo-1-naphthalenyl)azo]-2,7-naphthalenedisulfonic acid complex (CAS No. 12227-62-2)) was estimated using EPI suite KOCWIN Program (v2.00) as 1260000 L/kg (log Koc= 6.1003) by means of MCI method at 25 deg. C. This log Koc value indicates that test chemical Aluminium, 3-hydroxy-4-[(4-sulfo-1-naphthalenyl)azo]-2,7-naphthalenedisulfonic acid complex has very strong sorption to soil and therefore test chemical has negligible migration potential to ground water.
- Executive summary:
The Soil Adsorption Coefficient i.e. Koc value of test chemical Aluminium, 3-hydroxy-4-[(4-sulfo-1-naphthalenyl)azo]-2,7-naphthalenedisulfonic acid complex (CAS No. 12227-62-2)) was estimated using EPI suite KOCWIN Program (v2.00) as 1260000 L/kg (log Koc= 6.1003) by means of MCI method at 25 deg. C. This log Koc value indicates that test chemical Aluminium, 3-hydroxy-4-[(4-sulfo-1-naphthalenyl)azo]-2,7-naphthalenedisulfonic acid complex has very strong sorption to soil and therefore test chemical has negligible migration potential to ground water.
Reference
Description of key information
The Soil Adsorption Coefficient i.e. Koc value of test chemical Aluminium, 3-hydroxy-4-[(4-sulfo-1-naphthalenyl)azo]-2,7-naphthalenedisulfonic acid complex (CAS No. 12227-62-2)) was estimated using EPI suite KOCWIN Program (v2.00) as 1260000 L/kg (log Koc= 6.1003) by means of MCI method at 25 deg. C. This log Koc value indicates that test chemical Aluminium, 3-hydroxy-4-[(4-sulfo-1-naphthalenyl)azo]-2,7-naphthalenedisulfonic acid complex has very strong sorption to soil and therefore test chemical has negligible migration potential to ground water.
Key value for chemical safety assessment
- Koc at 20 °C:
- 1 260 000
Additional information
Predicted data study for target chemical Aluminium, 3-hydroxy-4-[(4-sulfo-1-naphthalenyl)azo]-2,7-naphthalenedisulfonic acid complex (CAS No. 12227-62-2) and supporting experimental study for its structurally similar read cross chemical have been conducted for adsorption endpoint and their results are summarized below.
In predicted data study the Soil Adsorption Coefficient i.e. Koc value of test chemical Aluminium, 3-hydroxy-4-[(4-sulfo-1-naphthalenyl)azo]-2,7-naphthalenedisulfonic acid complex (CAS No. 12227-62-2) was estimated using Estimation Program Interface (EPI suite, 2017) KOCWIN Program (v2.00) as 1260000 L/kg (log Koc= 6.1003) by means of MCI method at 25 deg. C. This log Koc value indicates that test chemical Aluminium, 3-hydroxy-4-[(4-sulfo-1-naphthalenyl)azo]-2,7-naphthalenedisulfonic acid complex has very strong sorption to soil and therefore test chemical has negligible migration potential to ground water.
Another study was experimental study for read across chemical trisodium (4E)-3-oxo-4-[2-(4-sulfonatonaphthalen-1-yl)hydrazin-1-ylidene]-3,4-dihydronaphthalene-2,7-disulfonate (CAS no. 915 -67 -3) Amaranth dye from Research Journal of Chemical Sciences, by Nanganoa L.T, Ketcha J.M. and Ndi J.N. (2014) in this study the capability of smectite clay (Sa01) was investigated as a low cost adsorbent for the adsorption of a hazardous water soluble dye amaranth from aqueous solutions.
The clay material obtained from Sabga in the North West region of Cameroon (Sa01).Sa01 was air dried, ground into fine powder using a mortar and was then passed through an 80 μm mesh opening size sieve. The sieved powder was kept in an oven at 110°C for 24 hours, removed and cooled in a dessicator before use.
The experiments were conducted with artificial wastewater solution prepared by dissolving amaranth dye in distilled water. A 1000 mg/L stock solution of amaranth was prepared. By dilution with distilled water, standard solutions were also prepared. The concentrations of these solutions were measured with a UV spectrophotometer at a wavelength of maximum absorption of 520 nm. A calibration curve of absorbance versus concentration of the dye was plotted. The pH of the solutions was adjusted with either 0.1 M HCl or 0.1 M NaOH.
Batch mode adsorption studies were performed at ambient temperature of 25°C. Solutions containing known concentrations of adsorbate and accurately weighed amounts of adsorbent were introduced in 250 ml capacity flasks, sealed and agitated with a magnetic stirrer at given time intervals.
Two types of isotherm models were investigated; the Langmuir and Freundlich Isotherms.
83.6% of dye was adsorbed at pH 2, adsorbent mass of 1.0 g and initial dye concentration of 30 mg/L.
kf =0.281, kl = 0.0822
kf = freundlich adsorption isotherm constant
kl = Langmuir adsorption isotherm constant
The Freundlich adsorption isotherm was observed to correlate better the experimental data with R2 = 0.9894.
On the basis of both the studies mentioned above it can be concluded that test chemical test chemical Aluminium, 3-hydroxy-4-[(4-sulfo-1-naphthalenyl)azo]-2,7-naphthalenedisulfonic acid complex has very strong sorption to soil and therefore test chemical has negligible migration potential to ground water.
[LogKoc: 6.1003]
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