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EC number: 243-717-6 | CAS number: 20298-05-9
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
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- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
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- Solubility in organic solvents / fat solubility
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- 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
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- Nanomaterial aspect ratio / shape
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- Nanomaterial Zeta potential
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- Nanomaterial photocatalytic activity
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- 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:
Half life of hydrolysis of test chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate (CAS no.20298-05-9) was estimated by using OECD QSAR tool box v3.3 considering five closest read across chemicals with log Kow as primary descriptor. The half life of hydrolysis of test chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate was estimated to be 314.275 days. On the basis of this half life value it is concluded that test chemical is not hydrolysable.
Biodegradation:
Biodegradation in water:
Biodegradability of test chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate
(CAS no. 20298 -05 -9) was estimated by using OECD QSAR tool box v3.3 considering eight closest read across chemical with log Kow as primary descriptor. Percent biodegradation of test chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate was estimated to be 0.75 by considering BOD as parameter and microorganisms as inoculum in 28 days. On the basis of percent biodegradability value it is concluded that this test chemical is not readily biodegradable.
Bioaccumulation:
Bioaccumuation: aquatic/sediments:
Using BCFBAF Program (v3.00) model of EPI suite 2017 the estimated bio concentration factor (BCF) for Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate (CAS No. 20298-05-9) 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-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate is non bioaccumulative in food chain.
Transport and distribution:
Adsorption/desorption:
The Soil Adsorption Coefficient i.e. Koc value of test chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate (CAS No. 20298-05-9) was estimated using EPI suite KOCWIN Program (v2.00) as 12850 L/kg (log Koc= 4.10) by means of MCI method at 25 deg. C. This log Koc value indicates that test chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate has strong sorption to soil and therefore have negligible to slow migration potential to ground water.
Additional information
Stability:
Hydrolysis:
Predicted data for target chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate (CAS no.20298-05-9) and experimental studies for its read across chemical are summarized below for hydrolysis endpoint.
In first weight of evidence study the Half life of hydrolysis of test chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate (CAS no.20298-05-9) was estimated by using OECD QSAR tool box v3.3 considering five closest read across chemicals with log Kow as primary descriptor. The half life of hydrolysis of test chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate was estimated to be 314.275 days. On the basis of this half life value it is concluded that test chemical is not hydrolysable.
Another weight of evidence study for was done from authoritative database (HSDB, 2017) in this study the read across chemical trisodium 5-hydroxy-1-(4-sulphophenyl)-4-(4-sulphophenylazo)pyrazole-3-carboxylate (CAS no. 1934 -21 -0) is not expected to undergo hydrolysis in the environment due to the lack of functional groups that hydrolyze under environmental conditions On the basis of this it is concluded that this read across chemical is not hydrolysable.
Last weight of evidence study was also done from same authoritative database in this study the read across chemical disodium 6-hydroxy-5-[(4-sulfonatophenyl)diazenyl]naphthalene-2-sulfonate (CAS no.2783-94-0) is not expected to undergo hydrolysis in the environment due to the lack of functional groups that hydrolyze under environmental conditions On the basis of this it is concluded that this read across chemical is not hydrolysable.
On the basis of all the studies mentioned above it can be concluded that test chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate (CAS no.20298-05-9) is not hydrolysable.
Biodegradation:
Biodegradation in water:
Predicted data for target chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate(CAS no. 20298 -05 -9) and experimental studies for its read across chemical are summarized below for biodegradation endpoint.
In first weight of evidence study the biodegradability of test chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate(CAS no. 20298 -05 -9) was estimated by using OECD QSAR tool box v3.3 considering eight closest read across chemical with log Kow as primary descriptor. Percent biodegradation of test chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate was estimated to be 0.75 by considering BOD as parameter and microorganisms as inoculum in 28 days. On the basis of percent biodegradability value it is concluded that this test chemical is not readily biodegradable.
Another weight of evidence study was done from Chemosphere Vol 22 pp 107-119 1991 by Glenn M Shaul, Thomas J Holdsworth, Clyde R. Dempsey, and Kenneth A. Dostal in this study the Biodegradability of read across chemical trisodium 5-hydroxy-1-(4-sulphophenyl)-4-(4-sulphophenylazo)pyrazole-3-carboxylate (Acid yellow 23) was determined by anlysing percent recovery of test material. This read across material is dye and inoculums used for biodegradation was obtained from Screened raw waste water from greater Cincinnati Mill Creek sewage treatment plant was used as influent (INF) to three pilot scale activated sludge biological treatment systems (Two experimental and one control). Each system consists of primary clarifier, complete mix aeration basin and secondary clarifier. Influent was spiked with test material at concentration of 1 mg/L and 5 mg/L. Then Dye analytical studies were conducted by purified dye compound in organic free influent waste water and mixed liquor. Then influent, primary influent filtrate was passed through column packed with resin. The filter paper and resin were soaked in an ammonia – acetonitrile solution and then soxhlet extracted with ammonia – acetonitrile. The extract was concentrated and brought upto 50 ml volumn with methanol/dimethyl formamaide solution. All extracted samples were analyzed by HPLC with ultraviolet detector. Percent recovery determined was 107 % in low spiked and 103 % in high spiked. On the basis of percent recovery value biodegradation of dye was negligible i.e., 0%. Percent biodegradation of read across chemical trisodium 5-hydroxy-1-(4-sulphophenyl)-4-(4-sulphophenylazo)pyrazole-3-carboxylatewas observed to be 0.0 % by test material analysis by HPLC parameter. On the basis of percent degradation it is concluded that this test material is not readily biodegradable.
Next weight of evidence study was done from The Journal of Toxicological Sciences, Vol.3 , 193 -204, (1978) by Yasuhide TONOGAI, Masahiro IWAIDA, Masatomo TATI, Youki OsE and Takahiko SATO . The aim of the study was to estimate the microbial decomposition of read across chemical Food yellow 4 dye. The biodegradation of chemical was determined by 3 methods under aerobic conditions: Aerobic decomposition of dyes with sludge, Oxygen uptake and BOD determination.
During 10 days of the aerobic experiment, the absorbance of dye solution was measured once in a day for 10 days. 20% decomposition of read across chemical was obtained in 10 days. 3.82 O2 mg/hg – sludge oxygen uptake was obtained in 5 –hrs test and the dissolved oxygen contents on the 5th day were essentially the same to initial ones. The low reactivity of aerobic sludge towards dyes was confirmed.
Based on the results obtained from the aerobic degradation assay, Warburg method and BOD determination it can be concluded that this read across is not readily biodegradable under aerobic conditions.
Next study was also conducted for read across from the Journal of Toxicological Sciences, Vol.3 , 193 -204, (1978) in this study the Biodegradability of read across chemical Sodium 4-(4-(2-hydroxynaphthalenylazo)phenylazo) benzenesulphonate (Acid Red 151) was determined by analyzing percent recovery of test material. This test material is dye and inoculums used for biodegradation was obtained from Screened raw waste water from greater Cincinnati Mill Creek sewage treatment plant was used as influent (INF) to three pilot scale activated sludge biological treatment systems (Two experimental and one control). Each system consists of primary clarifier, complete mix aeration basin and secondary clarifier. Influent was spiked with test material at concentration of 1 mg/L and 5 mg/L. Then Dye analytical studies were conducted by purified dye compound in organic free influent waste water and mixed liquor. Then influent, primary influent filtrate was passed through column packed with resin. The filter paper and resin were soaked in an ammonia – acetonitrile solution and then soxhlet extracted with ammonia – acetonitrile. The extract was concentrated and brought upto 50 ml volumn with methanol/dimethyl formamaide solution. All extracted samples were analyzed by HPLC with ultraviolet detector. Percent recovery and Percent adsorbed of read across chemical Sodium 4-(4-(2-hydroxynaphthalenylazo)phenylazo)benzenesulphonatewas observed was 82% and 50 % in low spike of test chemical and 70 % and 58% at high spike of read across chemical respectively. On the basis of percent recovery value biodegradation of dye was 9.0 % at low spike and 15 % at high spike of read across chemical. On the basis of percent degradation it is concluded that this read across material is not readily biodegradable.
Last weight of evidence study was done from authoritative database (HSDB, 2017) in this study the read across chemical disodium 6-hydroxy-5-[(4-sulfonatophenyl)diazenyl]naphthalene-2-sulfonate (CAS no. 2783-94-0) showed 0.0% biodegradation by considering BOD as parameter in 5 days, and by taking sewage as inoculums. So it is concluded that read across chemical disodium 6-hydroxy-5-[(4-sulfonatophenyl)diazenyl]naphthalene-2-sulfonate is not readily biodegradable.
On the basis of all the studies mentioned above it can be concluded that test chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate (CAS No. 20298-05-9) is expected to be not readily biodegradable.
Bioaccumulation:
Bioaccumuation: aquatic/sediments:
Predicted data study for target chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate (CAS No. 20298-05-9) and two experimental studies for its structurally similar read across
Chemicals are summarized below.
The first weight of evidence study was done by Using BCFBAF Program (v3.00) model of Estimation Program Interface (EPI suite 2017) the estimated bio concentration factor (BCF) for Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate (CAS No. 20298-05-9) 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-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate is non bioaccumulative in food chain.
Next weight of evidenc e study was done by using authoritative database (Jcheck, 2017) in this study the bioaccumulation test was conducted for 6 weeks for determination the bioconcentration factor (BCF) of read across chemical trisodium 5-hydroxy-1-(4-sulphophenyl)-4-(4-sulphophenylazo)pyrazole-3-carboxylate (CAS no 1934-21-0) on test organism Cyprinus carpio. Recovery ratio of Test water was at 1st concentration area : 91.7 % and at 2nd concentration area : 83 .0%, Fish : 90.6 %, and Limit of detection in Fish was 0.17 mg/L Nominal concentrations used was 1st Concentration area: 0.6 mg/L (w/v), 2nd Concentration area: 0.06 mg/L (w/v) and Range finding study was carried out on Rice fish (Oryzias latipes) TLm(48h) ≥ 1000 ppm(w/v). The lipid content of fish was 2.8 %.
Thus according to static Fish test the BCF value for trisodium 5-hydroxy-1-(4-sulphophenyl)-4-(4-sulphophenylazo)pyrazole-3-carboxylate was observed to be ≤0.29 L/kg at dose concentration 0.6 mg/L and ≤ 3 L/kg at dose concentration 0.06 mg/L on test organism Cyprinus carpio during 6 weeks period.
These BCF values indicate that the substance trisodium 5-hydroxy-1-(4-sulphophenyl)-4-(4-sulphophenylazo)pyrazole-3-carboxylate is not bioaccumulative in fish and food chain as these values are far less than 2000 criteria.
Last weight of evidence study was also done from authoritative database (HSDB, 2017) in this study the ionic character of read across chemical disodium 6-hydroxy-5-[(4-sulfonatophenyl)diazenyl]naphthalene-2-sulfonate(CAS no. 2783-94-0) suggests the potential for bioconcentration in aquatic organisms is expected to be low.
On the basis of all the studies mentioned above it can be concluded that test chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate (CAS No. 20298-05-9) is expected to be non bioaccumulative in nature.
Transport and distribution:
Adsorption/desorption:
The Soil Adsorption Coefficient i.e. Koc value of test chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate (CAS No. 20298-05-9) was estimated using EPI suite KOCWIN Program (v2.00) as 12850 L/kg (log Koc= 4.10) by means of MCI method at 25 deg. C. This log Koc value indicates that test chemical Trisodium 2-[(E)-2-(3-methyl-5-oxo-1-{4-[2-(sulfonatooxy)ethanesulfonyl]phenyl}-4,5-dihydro-1H-pyrazol-4-yl)diazen-1-yl]naphthalene-1,5-disulfonate has strong sorption to soil and therefore have negligible to slow migration potential to ground water.
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