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disodium 5-{4-chloro-6-[N-ethyl-3-(vinylsulfonyl)anilino]-1,3,5-triazin-2-ylamino}-4-hydroxy-3-[(4-vinylsulfonyl)phenylazo]naphthalene-2,7-disulfonate; reaction mass of: trisodium 5-{4-chloro-6-[N-ethyl-(3-(2-sulfonatooxy)ethylsulfonyl)anilino]-1,3,5-triazin-2-ylamino}-4-hydroxy-3-[4-(vinylsulfonyl)phenylazo]naphthalene-2,7-disulfonate; tetrasodium 5-{4-chloro-6-[N-ethyl-3-(2-(sulfonatooxy)ethylsulfonyl)anilino]-1,3,5-triazin-2-ylamino}-3-[4-(2-(sulfonatooxy)ethylsulfonyl)phenylazo]-4-hydroxynaphthalene-2,7-disulfonate; trisodium 5-{4-chloro-6-[N-ethyl-3-(vinylsulfonyl)anilino]-1,3,5-triazin-2-ylamino}-4-hydroxy-3-[4-(2-(sulfonatooxy)ethylsulfonyl)phenylazo]naphthalene-2,7-disulfonate
EC number: 444-050-5 | 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
Toxicity to microorganisms
Administrative data
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- June 10, 2002- October 7, 2002
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 002
- Report date:
- 2002
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- Version / remarks:
- 1984
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.11 (Biodegradation: Activated Sludge Respiration Inhibition Test)
- Version / remarks:
- 1988
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- -
- EC Number:
- 444-050-5
- EC Name:
- -
- IUPAC Name:
- dodecasodium 5-({4-chloro-6-[ethyl({3-[2-(sulfooxy)ethanesulfonyl]phenyl})amino]-1,3,5-triazin-2-yl}amino)-3-[(E)-2-[4-(ethenesulfonyl)phenyl]diazen-1-yl]-4-hydroxynaphthalene-2,7-disulfonate 5-({4-chloro-6-[ethyl({3-[2-(sulfooxy)ethanesulfonyl]phenyl})amino]-1,3,5-triazin-2-yl}amino)-4-hydroxy-3-[(E)-2-{4-[2-(sulfooxy)ethanesulfonyl]phenyl}diazen-1-yl]naphthalene-2,7-disulfonate 5-[(4-chloro-6-{[3-(ethenesulfonyl)phenyl](ethyl)amino}-1,3,5-triazin-2-yl)amino]-3-[(E)-2-[4-(ethenesulfonyl)phenyl]diazen-1-yl]-4-hydroxynaphthalene-2,7-disulfonate 5-[(4-chloro-6-{[3-(ethenesulfonyl)phenyl](ethyl)amino}-1,3,5-triazin-2-yl)amino]-4-hydroxy-3-[(E)-2-{4-[2-(sulfooxy)ethanesulfonyl]phenyl}diazen-1-yl]naphthalene-2,7-disulfonate
- Test material form:
- solid
- Details on test material:
- Identity: Red Rwa 4565
Appearance: Solid, red powder
Storage: at room temperature at about 20°C
Constituent 1
Sampling and analysis
- Analytical monitoring:
- no
- Details on sampling:
- No data.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- Please refer to "Details on test conditions" and "Any other information on materials and methods".
Test organisms
- Test organisms (species):
- activated sludge of a predominantly domestic sewage
- Details on inoculum:
- - Name and location of sewage treatment plant where inoculum was collected: aerobic activated sludge from a wastewater treatment plant (ARA Ergolz II, Fullinsdorf, Switzerland) treating predominantly domestic wastewater.
- Preparation of inoculum for exposure:
During the holding of two days prior to use, the sludge was fed daily with 50 mL synthetic wastewater* per liter and was kept at room temperature under continuous aeration until use. lmmediately before use, the dry weight of the activated sludge was measured again in the inoculum used in the test. The pH of the activated sludge inoculum was adjusted from 8.1 to 7.1 with a diluted sulfuric acid solution.
- Pretreatment:
The sludge was washed twice with tap water by centrifugation and the supernatant liquid phase was decanted. A homogenized aliquot of the final sludge suspension was weighed, thereafter dried and the ratio of wet to dry weight was calculated. Based on this ratio, an aliquot of washed sludge was suspended in tap water to obtain a concentration equivalent to 3 g dry material per liter.
*Synthetic wastewater: [16 g peptone; 11 g meat extract; 3 g urea; 0.7 g NaCl; 0.4 g CaCl2 · 2H20; 0.2 g MgS04 · 7H20; 2.8 g K2HP04] filled up to a final volume of 1 liter with deionized water.
Study design
- Test type:
- static
- Water media type:
- other: Tap water and synthetic wastewater
- Limit test:
- no
- Total exposure duration:
- 3 h
- Remarks on exposure duration:
- None
- Post exposure observation period:
- None
Test conditions
- Hardness:
- Not specified.
- Test temperature:
- The water temperature was measured in one control at the start and at the end of the incubation period, and was continuously monitored in all test media and the controls during measurement of the respiration rate.
- pH:
- The pH values and the dissolved oxygen concentrations were determined in all test media and the controls at the start and at the end of the 3-hour incubation period.
- Dissolved oxygen:
- During the incubation period of exactly 3 hours all test media and the controls were continuously aerated by intense stirring on magnetic stirrers. The concentration of dissolved oxygen did not drop below 2.5 mglL during the incubation period, and just before measurement of the respiration rates the dissolved oxygen concentrations were at least 6.9 mg/L.
- Salinity:
- Not specified
- Conductivity:
- Not specified
- Nominal and measured concentrations:
- Nominal concentrations: 10, 32, 100, 320 and 1000 mg/L.Concentrations exceeding 1000 mg/L were not tested.
According to the results of a pre-test (non-GLP), no stock solution could be prepared due to the insufficient water solubility of Red Rwa 4565.
Therefore, test item amounts of 5.0, 16.1, 51.0, 160.2 and 500.2 mg were directly weighed (by means of an analytical balance) into the test flasks. Then 284 mL of tap water was added to each flask. The test item was mixed into the tap water by ultrasonic treatment for ten minutes and intense stirring Íor 24 hours at roomtemperature in the dark to dissolve a maximum amount of the test item ancl/or disperse it as homogeneously as possible. Then,16 mL of synthetic wastewater and 200 mL of the activated sludge inoculum were added.
Additionally, two controls (tap water, synthetic wastewater and activated sludge inoculum, without test item) and the reference item 3,S-dichlorophenol (positive control) at nominal concentrations of 5, 16 and 50 mg/L were tested in parallel under otherwise identical test conditions. - Details on test conditions:
- TEST SYSTEM
- Test vessel: 1000 mL glass flasks
- Aeration: During the incubation period of exactly 3 hours all test media and the controls were continuously aerated by intense stirring on magnetic stirrers. The concentration of dissolved oxygen did not drop below 2.5 mglL during the incubation period, and just before measurement of the respiration rates the dissolved oxygen concentrations were at least 6.9 mg/L
- Sludge concentration (weight of dry solids per volume): At the start of the test 200 ml activated sludge inoculum with a sludge concentration of 2.3 g dry weight/l (corresponding to about 0.9 g dry material per liter test medium) was added. The sludge was added in time intervals of 15 minutes (an arbitrary but convenient interval) first to a control, then to the test solutions of the reference item, then to the test solutions of the test item, and finally to the second control.
TEST CONCENTRATIONS
- Test concentrations: 10, 32, 100, 320 & 1000 mg/L
Results and discussion
Effect concentrationsopen allclose all
- Key result
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Key result
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Duration:
- 3 h
- Dose descriptor:
- other: EC20
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Duration:
- 3 h
- Dose descriptor:
- other: EC80
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Details on results:
- The test item Red Rwa 4565 had no significant inhibitory etfect (<15%) on the respiration rate of activated sludge after the incubation period of three hours up to and including the highest test item concentration of 1000 mg/L. Thus, the 3-hour NOEC of Red Rwa 4565 to activated sludge microorganisms was at least 1000 mg/L. This value might be even higher, but concentrations exceeding 1000 mg/L were not tested. The 3-hour 8C20, EC50 and EC80 could not be calculated, but were clearly higher than 1000 mg/L.
- Results with reference substance (positive control):
- The 3-hour EC50 of the reference item 3,S-dichlorophenol (positive control) was calculated to be 13mg/L (the 95% confidence limits were not calculable). The 3-hour EC50 is within the guideline-recommended range of 5-30 mg/L, confirming suitability of the activated sludge used.
- Reported statistics and error estimates:
- No statistical analysis was performed.
Any other information on results incl. tables
Influence of 3.5 -dichlorophenol and Red Rwa 4565 on oxygen consumption of activated sludge
Flask |
Test chemical |
Nominal concentration of test chemical (mg/L) |
Oxygen consumption rate (mg O2/L min-1) |
Inhibition (%) |
pH values |
Oxygen concentration (mg O2/L) |
|
||||||||
Start* |
End* |
Start* |
End* |
|
|||||||||||
1 |
control |
0 |
1.187 |
|
7.8 |
8.1 |
8.3 |
8.6 |
|
||||||
10 |
control |
0 |
1.187 |
|
7.7 |
7.8 |
8.5 |
6.9 |
|
||||||
Mean deviation (%) |
1.237 8.4 |
|
|
|
|
|
|||||||||
2 |
3,5-dichlorophenol |
5 |
1.113 |
10.0 |
7.8 |
8.1 |
8.5 |
8.7 |
|
||||||
3 |
3,5-dichlorophenol |
16 |
0.388 |
68.6 |
7.8 |
8.2 |
8.6 |
8.6 |
|
||||||
4 |
3,5-dichlorophenol |
50 |
0.113 |
90.8 |
7.7 |
8.3 |
8.6 |
8.6 |
|
||||||
5 |
Red Rwa 4565 |
10 |
1.254 |
-1.4 |
7.8 |
8.1 |
8.5 |
8.3 |
|
||||||
6 |
Red Rwa 4565 |
32 |
1.357 |
-9.7 |
7.8 |
8.0 |
8.6 |
8.2 |
|
||||||
7 |
Red Rwa 4565 |
100 |
1.249 |
-1.0 |
7.8 |
7.9 |
8.4 |
8.2 |
|
||||||
8 |
Red Rwa 4565 |
320 |
1.264 |
-2.2 |
7.8 |
7.9 |
8.6 |
8.4 |
|
||||||
9 |
Red Rwa 4565 |
1000 |
1.089 |
12.0 |
7.8 |
7.9 |
8.5 |
7.5 |
|
||||||
*Start and end of the 3-hour incubation period
- % inhibition: increased oxygen consumption rate relative to that of control
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- When Red Rwa 4565 was assessed for its toxicity to waste water bacteria, the following result was obtained:
- the 3-hour NOEC of Red Rwa 4565 to activated sludge microorganisms was at least 1000 mg/L;
- the 3-hour EC20, EC50 and EC80 could not be calculated, but were clearly higher than 1000 mg/L. - Executive summary:
The inhibitory effect of the test item Red Rwa 4565 on the respiration rate of aerobic wastewater microorganisms of activated sludge was investigated in a 3-hour respiration inhibition test according to the EU Commission Directive 87/302/EEC, and the OECD Guideline for Testing of Chemicals, No. 209.
The following nominal concentrations of Red Rwa 4565 were tested: 10, 32, 100, 320 and 1000 mg/L. Concentrations exceeding 1000 mg/L were not tested.
ln addition, two controls and three different concentrations of the reference item 3,5-dichlorophenol (5, 16 and 50 mg/L) were tested in parallel. The results of these treatments confirmed suitability of the activated sludge and the method used.
Up to and including the highest concentration of 1000 mg/L the test item Red Rwa 4565 had no significant inhibitory effect (<15%) on the respiration rate of activated sludge after the incubation period of three hours. Thus, the 3-hour NOEC of Red Rwa 4565 to activated sludge microorganisms was at least 1000 mg/L. This value might be even higher, but concentrations exceeding 1000 mg/L were not tested. The 3-hour EC20, EC50 and EC80 could not be calculated, but were clearly higher than 1000 mg/L.
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