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EC number: 282-941-9 | CAS number: 84473-86-9
- 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: screening tests
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with limited documentation / justification
- Justification for type of information:
- The supporting QMRF report has been attached.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 C (Ready Biodegradability: Modified MITI Test (I))
- Principles of method if other than guideline:
- Prediction was done using OECD QSAR tool box v.3.3
- GLP compliance:
- not specified
- Specific details on test material used for the study:
- - Name of test material : 3,4,5,6-tetrachloro-2-(2,4,5,7-tetrabromo-3,6-dihydroxyxanthen-9-yl)benzoic acid, aluminium salt
- Molecular formula : C20H4Br4Cl4O5.xAl
- Molecular weight : 2387.0295 g/mol
- Smiles notation : c1c2c(c(c(c1Br)O)Br)Oc3c(cc(c(c3Br)O)Br)C2c4c(c(c(c(c4Cl)Cl)Cl)Cl)C(=O)[O-].c1c2c(c(c(c1Br)O)Br)Oc3c(cc(c(c3Br)O)Br)C2c4c(c(c(c(c4Cl)Cl)Cl)Cl)C(=O)[O-].c1c2c(c(c(c1Br)O)Br)Oc3c(cc(c(c3Br)O)Br)C2c4c(c(c(c(c4Cl)Cl)Cl)Cl)C(=O)[O-].[Al+3]
- InChl: 1S/3C20H6Br4Cl4O5.Al/c3*21-5-1-3-7(8-9(20(31)32)13(26)15(28)14(27)12(8)25)4-2-6(22)17(30)11(24)19(4)33-18(3)10(23)16(5)29;/h3*1-2,7,29-30H,(H,31,32);/q;;;+3/p-3
- Substance type:Organic
- Physical state:Solid - Oxygen conditions:
- not specified
- Inoculum or test system:
- other: Microorganisms
- Duration of test (contact time):
- 28 d
- Parameter followed for biodegradation estimation:
- other: BOD
- Key result
- Parameter:
- other: BOD
- Value:
- 0.2
- Sampling time:
- 28 d
- Remarks on result:
- other: other details not available
- Details on results:
- The percent biodegradation estimated of test chemical 3,4,5,6-tetrachloro-2-(2,4,5,7-tetrabromo-3,6-dihydroxyxanthen-9-yl)benzoic acid, aluminium salt is 0.20% by taking BOD as parameter in 28 days.
- Validity criteria fulfilled:
- not specified
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- The percent biodegradability of test chemical 3,4,5,6-tetrachloro-2-(2,4,5,7-tetrabromo-3,6-dihydroxyxanthen-9-yl)benzoic acid, aluminium salt estimated was 0.20 % by taking BOD parameter into consideration and microorganism as a inoculum in 28 days. The percent degradation is very less so it is concluded that this test chemical is not readily biodegradable.
- Executive summary:
Biodegradability of test chemical is predicted using OECD QSAR tool box v.3.3 using log kow as a primary descriptor. The percent biodegradability of test chemical 3,4,5,6-tetrachloro-2-(2,4,5,7-tetrabromo-3,6-dihydroxyxanthen-9-yl)benzoic acid, aluminium salt ( CAS no. 84473 -86 -9) estimated was 0.20 % by taking BOD parameter into consideration and microorganisms as a inoculum in 28 days. The percent degradation is very less so it is concluded that this test chemical is not readily biodegradable.
Reference
The
prediction was based on dataset comprised from the following
descriptors: BOD
Estimation method: Takes average value from the 5 nearest neighbours
Domain logical expression:Result: In Domain
(((((("a"
or "b" or "c" or "d" or "e" )
or "f" or "g" )
and ("h"
and (
not "i")
)
)
and "j" )
and "k" )
and ("l"
and "m" )
)
Domain
logical expression index: "a"
Referential
boundary: The
target chemical should be classified as Aluminum Compounds AND Not
categorized by US-EPA New Chemical Categories
Domain
logical expression index: "b"
Referential
boundary: The
target chemical should be classified as Aromatic perhalogencarbons OR
Aryl OR Aryl halide OR Carboxylic acid OR Fused carbocyclic aromatic OR
Fused saturated heterocycles OR No functional group found OR Phenol OR
Xanthene by Organic Functional groups ONLY
Domain
logical expression index: "c"
Referential
boundary: The
target chemical should be classified as Aromatic perhalogencarbons OR
Aryl halide OR Carboxylic acid OR No functional group found OR
Overlapping groups OR Phenol OR Xanthene by Organic Functional groups
(nested) ONLY
Domain
logical expression index: "d"
Referential
boundary: The
target chemical should be classified as Acid, aromatic attach [-COOH] OR
Alcohol, olefinic attach [-OH] OR Aliphatic Carbon [CH] OR Aliphatic
Carbon, two phenyl attach [-C-] OR Aliphatic Oxygen, two aromatic
attach [-O-] OR Aluminium [Al] OR Aromatic Carbon [C] OR Bromine,
aromatic attach [-Br] OR Bromine, olefinic attach [-Br] OR Carbonyl,
olefinic attach [-C(=O)-] OR Carbonyl, one aromatic attach [-C(=O)-] OR
Chlorine, aromatic attach [-Cl] OR Chlorine, olefinic attach [-Cl] OR
Hydroxy, aromatic attach [-OH] OR Miscellaneous sulfide (=S) or oxide
(=O) OR Olefinic carbon [=CH- or =C<] OR Oxygen, one aromatic attach
[-O-] OR Oxygen, two olefinic attach [-O-] OR Tertiary Carbon by Organic
functional groups (US EPA) ONLY
Domain
logical expression index: "e"
Referential
boundary: The
target chemical should be classified as Aromatic compound OR Aryl
bromide OR Aryl chloride OR Aryl halide OR Carbonic acid derivative OR
Carboxylic acid OR Carboxylic acid derivative OR Diarylether OR Ether OR
Halogen derivative OR Heterocyclic compound OR Hydroxy compound OR No
functional group found OR Phenol by Organic functional groups, Norbert
Haider (checkmol) ONLY
Domain
logical expression index: "f"
Referential
boundary: The
target chemical should be classified as Class 4 (Compounds and groups of
compounds acting by a specific mechanism) OR Class 5 (Not possible to
classify according to these rules) by Acute aquatic toxicity
classification by Verhaar (Modified) ONLY
Domain
logical expression index: "g"
Referential
boundary: The
target chemical should be classified as Acid moiety OR Phenols, Poly OR
SHOULD NOT BE PROFILED by Aquatic toxicity classification by ECOSAR ONLY
Domain
logical expression index: "h"
Referential
boundary: The
target chemical should be classified as Aromatic acid [-C(=O)-OH] AND
Aromatic alcohol [-OH] AND Aromatic bromide [-Br] AND Aromatic
chloride [-CL] AND Aromatic ether [-O-aromatic carbon] AND
Aromatic-CH AND Aromatic-H AND Not calculated by Biodegradation
fragments (BioWIN MITI)
Domain
logical expression index: "i"
Referential
boundary: The
target chemical should be classified as Aldehyde [-CHO] OR Aliphatic
acid [-C(=O)-OH] OR Aliphatic alcohol [-OH] OR Aliphatic amine
[-NH2 or -NH-] OR Aliphatic bromide [-Br] OR Aliphatic chloride
[-CL] OR Aliphatic ether [C-O-C] OR Amide [-C(=O)-N or -C(=S)-N]
OR Aromatic amine [-NH2 or -NH-] OR Aromatic-CH2 OR Aromatic-CH3 OR
Azo group [-N=N-] OR -C=CH [alkenyl hydrogen] OR Carbon with 4 single
bonds & no hydrogens OR -CH - [cyclic] OR -CH- [linear] OR -CH2-
[cyclic] OR -CH2- [linear] OR Cyanide / Nitriles [-C#N] OR Ester
[-C(=O)-O-C] OR Fluorine [-F] OR Ketone [-C-C(=O)-C-] OR Methyl
[-CH3] OR Nitroso [-N-N=O] OR Pyridine ring OR Tin [Sn] OR Triazine
ring (symmetric) by Biodegradation fragments (BioWIN MITI)
Domain
logical expression index: "j"
Referential
boundary: The
target chemical should be classified as Moderate AND Very fast by
Bioaccumulation - metabolism half-lives ONLY
Domain
logical expression index: "k"
Referential
boundary: The
target chemical should be classified as High (Class III) by Toxic hazard
classification by Cramer (original) ONLY
Domain
logical expression index: "l"
Parametric
boundary:The
target chemical should have a value of Molecular weight which is >= 266
Da
Domain
logical expression index: "m"
Parametric
boundary:The
target chemical should have a value of Molecular weight which is <= 489
Da
Description of key information
Biodegradability of test chemical is predicted using OECD QSAR tool box v.3.3 using log kow as a primary descriptor. The percent biodegradability of test chemical 3,4,5,6-tetrachloro-2-(2,4,5,7-tetrabromo-3,6-dihydroxyxanthen-9-yl)benzoic acid, aluminium salt ( CAS no. 84473 -86 -9) estimated was 0.20 % by taking BOD parameter into consideration and microorganism as a inoculum in 28 days. The percent degradation is very less so it is concluded that this test chemical is not readily biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
Additional information
Predicted data from OECD QSAR tool box.v.3.3 for target chemical 3,4,5,6-tetrachloro-2-(2,4,5,7-tetrabromo-3,6-dihydroxyxanthen-9-yl)benzoic acid, aluminium salt ( CAS no. 84473 -86 -9) and supporting weight of evidence studies for target chemical’s closest read across chemicals with log Kow as a primary descriptor and structurally similar read across chemical were summarized as below.
Biodegradability of test chemical was predicted using OECD QSAR tool box v.3.3 using log kow as a primary descriptor. The percent biodegradability of test chemical 3,4,5,6-tetrachloro-2-(2,4,5,7-tetrabromo-3,6-dihydroxyxanthen-9-yl)benzoic acid, aluminium salt ( CAS no. 84473 -86 -9) estimated was 0.20 % by taking BOD parameter into consideration and microorganism as a inoculum in 28 days. The percent degradation is very less so it is concluded that this test chemical is not readily biodegradable.
The supporting weight of evidence study from authoritative database ( J check, 2017) for read across chemical pentabromophenol ( CAS no. 608-71-9) was carried out to test biodegradation. Biodegradation was analysed by using BOD and HPLC parameter and by taking sludge as inoculums at 30 mg/L concentration. The initial concentration of read across chemical was 100 mg/L and study design is of standard type. After 4 weeks (28 days) read across chemical showed 0% biodegradation by BOD and 1 % by HPLC so it is concluded that read across chemical pentabromophenol is not readily biodegradable
Another supporting weight of evidence study from same source as stated above ( J check 2017) was performed for read across chemical 5-chloro-2-(2,4-dichlorophenoxy)phenol (CAS no.3380-34-5) to test biodegradation by taking activated sludge as a inoculums at 30 mg/L concentration . Biodegradation was analyzed by using two parameters BOD and HPLC. The initial concentration of test chemical was 100 mg/L and study design is of standard type. After 4 weeks( 28 days) read across chemical 5-chloro-2-(2,4-dichlorophenoxy)phenol showed 0% and 1% biodegradation by BOD and HPLC parameters respectively. So it is concluded that this read across chemical 5-chloro-2-(2,4-dichlorophenoxy)phenol is not readily biodegradable.
Last study was done from the Journal of Toxicological Sciences, Vol.3 , 193 -204, 1978 for structurally similar read across chemical phloxine B in this study the biodegradability of phloxine B was studied using methods: Aerobic degradability, Warburg method and BOD measurement. Return activated sludge was obtained from the municipal sewage treatment plant, Nakahama, Osaka. Synthetic sewage preparation: Glucos, peptone and potassium dihydrogen phosphate, 30g each, were dissolved in 1 liter water and the pH was adjusted to pH 7.0 with sodium hydroxide. Seeded Dilution water: To 1 liter, 10 ml of supernatant of sludge was added. Aerobic biodegradation assay: To 750ml of sludge (MLSS ca, 3,000 ppm) 250 ml of O.03 M dye solution was added, and bubbled with air sufficiently at 20°C. 5ml sample was taken out once a day. After sampling 5ml synthetic sewage was added to the mixture. Each sample was filtered through filter paper and diluted twenty times prior to the spectrophotometric measurement at the absorption maximum within the visible range. The decrease of dyes concentration was expressed in terms of percent to the initial absorption. The experiment was carried out for 10 days. Oxygen uptake of sludge [Warburg Method]- 2.0 ml of sludge, 0.2 ml of 1000 ppm dye solution, and 0.2 ml of 20% potassium hydroxide were pipetted into the vessel, the side arm and central well, respectively. The sludge and the dye solution were mixed and the vessel was shaken at 25°C. The oxygen uptake was measured. The oxygen uptake by sludge alone was subtracted from those by dyes addition.
Determination of BOD – Dye solution (10, 20, and 40 ppm) were prepared with the seeded dilution water and kept at 20°C (Japanese Industrial Standards Committee, 1971). The dissolved oxygen contents were measured by a dissolved oxygen meter, because of the coloration of the solutions.
As there is no regulation on the color of the effluent by the Water Pollution Control Law, discharge of coloring materials is regulated by only BOD OR COD. The COD, BOD and absorbance at 245 and 545 nm (representing ultraviolet and the visible absorbance) of Phloxine B was studied. During 10 days of the aerobic experiment, the absorbance of dye solution was measured once day for 10 days. Food Red No. 104 was scarcely decreased. Free acids of Red No.104, was precipitated due to the slight acidity (pH 6-7) of the solution. Based on the results obtained from the studies, it can be concluded that Phloxine B is not readily biodegradable under aerobic conditions. Phloxine B was determined to be non- biodegradable in the anaerobic test also performed.
On the basis of above results of target chemical 3,4,5,6-tetrachloro-2-(2,4,5,7-tetrabromo-3,6-dihydroxyxanthen-9-yl)benzoic acid, aluminium salt from OECD QSAR tool box v.3.3 and its supporting weight of evidence studies from authoritative database and Journal of Toxicological Sciences it is concluded that this test chemical 3,4,5,6-tetrachloro-2-(2,4,5,7-tetrabromo-3,6-dihydroxyxanthen-9-yl)benzoic acid, aluminium salt is not readily biodegradable.
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