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EC number: 274-356-2 | CAS number: 70161-20-5
- 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
Stability :
Hydrolysis:
The half life of hydrolysis of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) (CAS no. 70161 -20 -5) was estimated by using OECD QSAR tool box v3.4 considering seven closest read across chemicals with log Kow as primary descriptor. The half life of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) was estimated to be 151.27 days. On the basi s of this half life value it is concluded that this test chemical is not hydrolysable.
Biodegradation:
Biodegradation in water:
Biodegradability of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) (CAS no.70161 -20 -5) was estimated by using OECD QSAR tool box v3.4 considering five closest read across chemicals with log kow as primary descriptor. Percent biodegradation of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) (CAS no. 70161-20-5) was estimated to be 0.7833 % by considering BOD as parameter and microorganisms as inoculum in 28 days. Based on this percent biodegradability value it is concluded that this test chemical is not readily biodegradable.
Biodegradation in water and sediments:
Estimation Programs Interface (EPI Suite, 2017) prediction model was run to predict the half-life in water and sediment for the test compound Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) (CAS No.70161-20-5). If released in to the environment, 1.09 % of the chemical will partition into water according to the Mackay fugacity model level III and the half-life period of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) in water is estimated to be 180 days (4320 hrs). The half-life (180 days estimated by EPI suite) indicates that the chemical is persistent in water and the exposure risk to aquatic animals is moderate to high whereas the half-life period of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) in sediment is estimated to be 1620.833 days (38900 hrs). Based on this half-life value, it indicates that test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) is persistent in sediment.
Biodegradation in soil:
The half-life period of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) (CAS No. 70161 -20 -5) in soil was estimated using Level III Fugacity Model by EPI Suite version 4.1 estimation database (EPI suite, 2017). If released into the environment, 59.2 % of the chemical will partition into soil according to the Mackay fugacity model level III. The half-life period of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) in soil is estimated to be 360 days (8640 hrs). Based on this half-life value of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-), it is concluded that the chemical is persistent in the soil environment and the exposure risk to soil dwelling animals is moderate to high.
Bioaccumulation:
Bioaccumulation:aquatic/sediment:
Using BCFBAF Program (v3.00) model of EPI suite 2017 the estimated bio concentration factor (BCF) for Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) (CAS No.70161-20-5) is 3.162 L/kg wet-wt at 25 deg. c which does not exceed the bioconcentration threshold of 2000. Therefore it is concluded that test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) is non bioaccumulative in food chain.
Transport and distribution:
Adsorption/desorption:
The study does not need to be conducted because the substance has a low octanol water partition coefficient log pow = -16.20 and adsorption potential of this substance is related to this parameter.
Additional information
Stability :
Hydrolysis:
The half life of hydrolysis of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) (CAS no. 70161 -20 -5) was estimated by using OECD QSAR tool box v3.4 considering seven closest read across chemicals with log Kow as primary descriptor. The half life of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) was estimated to be 151.27 days. On the basi s of this half life value it is concluded that this test chemical is not hydrolysable.
Biodegradation:
Biodegradation in water:
Predicted data study for target chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) (CAS no.70161 -20 -5) and two experimental studies for read across chemicals have been conducted and their results are summarized below for biodegradation endpoint.
In first weight of evidence study the biodegradability of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) (CAS no.70161 -20 -5) was estimated by using OECD QSAR tool box v3.4 considering five closest read across chemicals with log kow as primary descriptor. Percent biodegradation of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) (CAS no. 70161-20-5) was estimated to be 0.7833 % by considering BOD as parameter and microorganisms as inoculum in 28 days. Based on this percent biodegradability value it is concluded that this test chemical is not readily biodegradable.
Another experimental weight of evidence study was done from Unique Ecotox Research Laboratory ( 2016) in this study the 28-days Manometric respirometry test was used by following the OECD guideline 301 F to determine the ready biodegradability of the read across chemical aluminium, 2-(1,3-dihydro-3-oxo-5-sulfo-2H-indol-2-ylidene)-2,3-dihydro-3-oxo-1H-indole-5-sulfonic acid complex (CAS No. 16521 -38 -3). The test system included control, test item and reference item. The concentration of read across chemical and reference item (Sodium Benzoate) chosen for the study was and 30 mg/l, while that of inoculum was 10ml/l. ThOD (Theoretical oxygen demand) of read across chemical and reference item was determined by calculation. % Degradation was calculated using the values of BOD and ThOD for read across chemical item and reference item. The BOD28 value of aluminium, 2-(1,3-dihydro-3-oxo-5-sulfo-2H-indol-2-ylidene)-2,3-dihydro-3-oxo-1H-indole-5-sulfonic acid complex was observed to be 0.067 mgO2/mg. ThOD was calculated as 1.460 mgO2/mg. Accordingly, the % degradation of the read across chemical after 28 days of incubation at 20 ± 1°C according to manometric respirometry test was determined to be -4.566 %. Based on the results, the read across chemical, under the test conditions, was considered to be not readily biodegradable at 20 ± 1°C over a period of 28 days.
Last weight of evidence study was done by from authoritative database (J check, 2017) in this study the Biodegradation experiment was carried out of read across chemical 2-Chloro-4-ethylamine-6-isopropylamine-1,3,5-triazine (CAS no. 1912-24-9) by taking activated sludge as inoculums at 30 mg/L concentration . The initial concentration of read across chemical taken was 100 mg/L. Biodegradation was analyzed by using two parameters namely BOD and HPLC. The study design was of standard type. Percent biodegradation of read across chemical2-Chloro-4-ethylamine-6-isopropylamine-1,3,5-triazine was observed to be 1.0 % by both BOD and HPLC parameters in 28 days. Therefore it is concluded that read across chemical 2-Chloro-4-ethylamine-6-isopropylamine-1,3,5-triazine is not readily biodegradable.
On the basis of all the studies mentioned above it can be concluded that test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) (CAS no.70161 -20 -5) is not readily biodegradable.
Biodegradation in water and sediments:
Estimation Programs Interface (EPI Suite, 2017) prediction model was run to predict the half-life in water and sediment for the test compound Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) (CAS No.70161-20-5). If released in to the environment, 1.09 % of the chemical will partition into water according to the Mackay fugacity model level III and the half-life period of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) in water is estimated to be 180 days (4320 hrs). The half-life (180 days estimated by EPI suite) indicates that the chemical is persistent in water and the exposure risk to aquatic animals is moderate to high whereas the half-life period of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) in sediment is estimated to be 1620.833 days (38900 hrs). Based on this half-life value, it indicates that test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) is persistent in sediment.
Biodegradation in soil:
The half-life period of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) (CAS No. 70161 -20 -5) in soil was estimated using Level III Fugacity Model by EPI Suite version 4.1 estimation database (EPI suite, 2017). If released into the environment, 59.2 % of the chemical will partition into soil according to the Mackay fugacity model level III. The half-life period of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) in soil is estimated to be 360 days (8640 hrs). Based on this half-life value of test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-), it is concluded that the chemical is persistent in the soil environment and the exposure risk to soil dwelling animals is moderate to high.
Bioaccumulation:
Bioaccumulation:aquatic/sediment:
Using BCFBAF Program (v3.00) model of EPI suite 2017 the estimated bio concentration factor (BCF) for Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) (CAS No.70161-20-5) is 3.162 L/kg wet-wt at 25 deg. c which does not exceed the bioconcentration threshold of 2000. Therefore it is concluded that test chemical Trisodium [2-[[α-[[2-hydroxy-5-sulpho-3-[(2,5,6-trichloro-4-pyrimidinyl)amino]phenyl]azo]benzyl]azo]-5-sulphobenzoato(5-)]cuprate(3-) is non bioaccumulative in food chain.
Transport and distribution:
Adsorption/desorption:
The study does not need to be conducted because the substance has a low octanol water partition coefficient log pow = -16.20 and adsorption potential of this substance is related to this parameter.
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