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Reaction product of 3-[4-(2-aminoethylamino)-6-(4-sulfoanilino)-1,3,5-heterocycle-2-ylamino]benzensulfonic acid, ammonia water, sodium chloride and {mixture of [poly(1~4)chlorosulfonylphthalocyaninato-N29,N30,N31,N32]copper(II), [poly(1~3)chlorosulfonyl (tribenzo[b,g,l]pyrido[2,3-q]-5,10,15,20-tetraazaporphyrinato-N21,N22,N23,N24)]copper(II),[poly(1~2)chlorosulfonyl(dibenzol[b,g(or b,l)dipyrido[2,3(or 3,2)-l,q (or g,q)]-5,10,15,20-tetraazaporphyrinato-N21,N22,N23,N24)] copper(II) and [monochlorosulfonyl(benzo[b]tripyridol[2,3(or 3,2)-g,lq]-5,10,15,20- tetraazaporphyrinato- N21,N22,N23,N24)] copper(II)
EC number: - | 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
Hydrolysis
Administrative data
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 08 January 2009 to 07 February 2009
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted in compliance with agreed protocols, with no or minor deviations from standard test guidelines and/or minor methodological deficiencies, which do not affect the quality of relevant results.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 009
- Report date:
- 2009
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.7 (Degradation: Abiotic Degradation: Hydrolysis as a Function of pH)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Date of inspection: 19 August 2008; Date of signature: 04 March 2009
Test material
Reference
- Name:
- Unnamed
- Type:
- Constituent
- Details on test material:
- Sponsor's identification : H-CB sodium salt
Description : blue solid
Purity : 94.8%
Lot number : MB-2
Date received : 04 December 2008
Storage conditions : room temperature in the dark
- Radiolabelling:
- no
Study design
- Analytical monitoring:
- yes
Duration of testopen allclose all
- Duration:
- 120 h
- pH:
- 4
- Initial conc. measured:
- 0.955 g/L
- Duration:
- 120 h
- pH:
- 7
- Initial conc. measured:
- 0.939 g/L
- Duration:
- 120 h
- pH:
- 7
- Initial conc. measured:
- 0.942 g/L
- Duration:
- 120 h
- pH:
- 9
- Initial conc. measured:
- 1 g/L
- Duration:
- 120 h
- pH:
- 9
- Initial conc. measured:
- 1.02 g/L
Results and discussion
- Transformation products:
- no
Dissipation DT50 of parent compoundopen allclose all
- pH:
- 4
- Temp.:
- 50 °C
- DT50:
- > 1 yr
- Remarks on result:
- other: Less than 10% hydrolysis after 5 days at 50°C, equivalent to a half-life greater than 1 year at 25°C, therefore no further testing was required.
- pH:
- 7
- Temp.:
- 50 °C
- DT50:
- > 1 yr
- Remarks on result:
- other: Less than 10% hydrolysis after 5 days at 50°C, equivalent to a half-life greater than 1 year at 25°C, therefore no further testing was required.
- pH:
- 9
- Temp.:
- 50 °C
- DT50:
- > 1 yr
- Remarks on result:
- other: Less than 10% hydrolysis after 5 days at 50°C, equivalent to a half-life greater than 1 year at 25°C, therefore no further testing was required.
Any other information on results incl. tables
The mean peak areas relating to the standard and sample solutions are shown in the following table:
Table 2
Solution |
MeanArea |
Standard 265 mg/l |
3.651 x 103 |
Standard 271 mg/l |
3.716 x 103 |
Initial Sample A, pH 4 |
3.284 x 103 |
Initial Sample B, pH 4 |
3.260 x 103 |
Standard 265 mg/l |
3.665 x 103 |
Standard 271 mg/l |
3.739 x 103 |
Initial Sample A, pH 7 |
3.232 x 103 |
Initial Sample B, pH 7 |
3.242 x 103 |
Standard 265 mg/l |
3.676 x 103 |
Standard 271 mg/l |
3.735 x 103 |
Initial Sample A, pH 9 |
3.479 x 103 |
Initial Sample B, pH 9 |
3.504 x 103 |
Standard 251 mg/l |
3.438 x 103 |
Standard 254 mg/l |
3.498 x 103 |
120 Hour Sample A, pH 4 |
3.281 x 103 |
120 Hour Sample B, pH 4 |
3.284 x 103 |
Standard 251 mg/l |
3.460 x 103 |
Standard 254 mg/l |
3.509 x 103 |
120 Hour Sample A, pH 7 |
3.244 x 103 |
120 Hour Sample B, pH 7 |
3.253 x 103 |
Standard 251 mg/l |
3.459 x 103 |
Standard 254 mg/l |
3.497 x 103 |
120 Hour Sample A, pH 9 |
3.462 x 103 |
120 Hour Sample B, pH 9 |
3.498 x 103 |
The test material concentrations at the given time points are shown in the following tables:
Table 3 pH 4 at 50.0 ± 0.5ºC
Time (Hours) |
Concentration (g/l) |
% of mean initial concentration |
|||||||
A |
B |
A |
B |
||||||
0 |
0.956 |
0.949 |
100 |
99.6 |
|||||
120 |
0.955 |
0.955 |
100 |
100 |
Result: Less than 10% hydrolysis after 5 days at 50°C, equivalent to a half-life greater than 1 year at 25°C, therefore no further testing was required.
Table 4 pH 7 at 50.0 ± 0.5ºC
Time (Hours) |
Concentration (g/l) |
% of mean initial concentration |
||
A |
B |
A |
B |
|
0 |
0.936 |
0.939 |
99.9 |
100 |
120 |
0.939 |
0.942 |
100 |
100 |
Result: Less than 10% hydrolysis after 5 days at 50°C, equivalent to a half-life greater than 1 year at 25°C, therefore no further testing was required.
Table 5 pH 9 at 50.0 ± 0.5ºC
Time (Hours) |
Concentration (g/l) |
% of mean initial concentration |
||
A |
B |
A |
B |
|
0 |
1.01 |
1.01 |
99.6 |
100 |
120 |
1.00 |
1.02 |
99.4 |
100 |
Result: Less than 10% hydrolysis after 5 days at 50°C, equivalent to a half-life greater than 1 year at 25°C, therefore no further testing was required.
Validation
The linearity of the detector response with respect to concentration was assessed over the nominal concentration range of 0 to 500 mg/l. This was satisfactory with a correlation coefficient of 1.000 being obtained.
Discussion
No significant peaks were observed at the approximate retention time of the test material on analysis of any matrix blank solutions and it was considered not necessary to do a blank subtraction from the standard and sample chromatograms.
Additionally, one example for each pH of the diluted 120 hour timepoint samples and 120 hour timepoint analysis standards was further diluted by a factor of 50 with reverse osmosis water. These were scanned in 10 mm quartz cells on a Perkin-Elmer Lambda 20 from 200 nm to 900nm using reverse osmosis water as the reference. There was no significant difference between applicable standard and sample where the test material adsorbed in the visible spectrum range with respect to both wavelength and intensity. This provides extra evidence that the test material did not hydrolyse under the test conditions. Any significant hydrolysis would probably have altered the adsorption characteristics (wavelength and/or intensity) of the test material.
As the test material was determined to be hydrolytically stable under acidic conditions (t½ > 1 year at 25°C) no additional testing was performed at pH 1.2, 37.0 ± 0.5°C.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- The estimated half-life at 25°C of the test material for pH 4, pH 7 and pH 9 has been shown to be >1 year.
- Executive summary:
The estimated half-life at 25°C of the test material for pH 4, pH 7 and pH 9 has been shown to be >1 year using Method C7 Abiotic Degradation, Hydrolysis as a Function of pH of Commission Regulation (EC) No 440/2008 of 30 May 2008
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