Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 271-176-6 | CAS number: 68516-73-4
- 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 soil
Administrative data
- Endpoint:
- biodegradation in soil: simulation testing
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- other:
- Justification for type of information:
- JUSTIFICATION FOR DATA WAIVING
see attached justification
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- data waiving: supporting information
Reference
- Endpoint:
- biodegradation in water: ready biodegradability
- 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, but not (completely) falling into its applicability domain, with adequate and reliable documentation / justification
- Principles of method if other than guideline:
- Estimation of results of OECD screening tests on ready biodegradation in water: CATALOGIC (v5.11.5) BOD 28 days MITI (OECD 301C) v06.07
- GLP compliance:
- no
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Duration of test (contact time):
- 28 d
- Parameter:
- % degradation (O2 consumption)
- Value:
- ca. 32.35
- Sampling time:
- 28 d
- Details on results:
- Model domain similarity:
- Parametric domain: 100%
- Structural domain: 61.54% (38.46% unknown)
- Mechanistic domain: 100% - Validity criteria fulfilled:
- yes
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- The test substance is not readily biodegradable (according to OECD criteria)
- Reason / purpose for cross-reference:
- data waiving: supporting information
Reference
- Endpoint:
- biodegradation in water: ready biodegradability
- 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, but not (completely) falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- Please refer to QMRF and QPRF in the section "Overall remarks" and "Executive summary", respectively.
- Principles of method if other than guideline:
- Prediction of ready biodegradability based on six QSAR models
- GLP compliance:
- no
- Key result
- Remarks on result:
- other: Ready biodegradability prediction: Substance is not readily biodegradable.
- Remarks on result:
- other: Biowin1: Biodegrades Fast; Biowin2: Does Not Biodegrade Fast; Biowin3: Recalcitrant; Biowin4: Days; Biowin5: Does Not Biodegrade Fast; BIOWIN6: Does Not Biodegrade Fast
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- not readily biodegradable
- Executive summary:
QPRF: BIOWIN v4.10
1.
Substance
See “Test material identity”
2.
General information
2.1
Date of QPRF
See “Data Source (Reference)”
2.2
QPRF author and contact details
See “Data Source (Reference)”
3.
Prediction
3.1
Endpoint
(OECD Principle 1)Endpoint
Biodegradability
Dependent variable
Biodegradability
3.2
Algorithm
(OECD Principle 2)Model or submodel name
BIOWIN
Model version
v. 4.10
Reference to QMRF
QMRF: Estimation of Aerobic Biodegradability using BIOWIN v4.10 (EPI Suite v4.11): BIOWIN1 to BIOWIN6 and Ready Biodegradability Prediction
Predicted value (model result)
See “Results and discussion”
Input for prediction
- Chemical structure via CAS number or SMILES
Descriptor values
- Structure fragments
- Molecular weight
3.3
Applicability domain
(OECD principle 3)Domains (Appendix D, On-Line BIOWIN User’s Guide):
1) Molecular weight
See below (Assessment of estimation domain)
2) Fragments:
See below (Assessment of estimation domain)
3.4
The uncertainty of the prediction
(OECD principle 4)Parameter
BIOWIN model
1
2
3
4
5
6
Total correct
264 / 295
275 / 295
167 / 200
165 / 200
485 / 589
488 / 589
% correct, total
89.5
93.2
83.5
82.5
82.3
82.9
% correct, fast
97.3 (181 / 186)
97.3 (181 / 186)
93.5 (101 / 108)
84.9 (101 / 119)
79.1 (201 / 254)
80.3 (204 / 254)
3.5
The chemical mechanisms according to the model underpinning the predicted result
(OECD principle 5)The chemical structure influences the biodegradability of the substance. Therefore, chemical fragments were selected having a potential effect on biodegradability. In order to be able to predict the biodegradability probability of substances without these specific fragments, the molecular weight was integrated into the models.
References
- US EPA (2012). On-Line BIOWIN User’s Guide.
Assessment of estimation domain (molecular weight, fragments):
Model:
BIOWIN v4.10
Substance:
tetramethyl 2,2'-{1,4-phenylenebis[imino(1,3-dioxobutane-2,1-diyl)diazene-2,1-diyl]}diterephthalate
CAS-#:
68516-73-4
SMILES:
CC(=O)C(N=Nc1c(ccc(c1)C(=O)OC)C(=O)OC)C(=O)Nc2ccc(cc2)NC(=O)C(N=Nc3c(
ccc(c3)C(=O)OC)C(=O)OC)C(=O)CMolecular weight (g/mol):
716.67
AppendixD - Fragment Coefficients for Biodegradation Models
BIOWIN1 and BIOWIN2: Linear / Non-Linear Biodegradability
Fragment description
Coefficient
Training set fragment count
No. of instances
of each bond
found for the
current substanceLinear
Non-linear
Min
Max
No. of compounds in training set containing the fragment
Ester [-C(=O)-O-C]
0.17418
4.0795
-
3
23
4
Amide [-C(=O)-N or -C(=S)-N]
0.21015
2.6913
-
1
12
2
Ketone [-C-C(=O)-C-]
0.00683
-0.453
-
2
12
2
Azo group [-N=N-]
-0.24183
-8.2194
-
1
2
2
Molecular Weight
---
---
31.06
697.7
out of range
BIOWIN3 and BIOWIN4: Ultimate / Primary biodegradability
Fragment description
Coefficient
Training set fragment count
No. of instances
of each bond
found for the
current substanceUltimate
Primary
Min
Max
No. of compounds in training set containing the fragment
Ester [-C(=O)-O-C]
0.14021
0.22896
-
4
25
4
Amide [-C(=O)-N or -C(=S)-N]
-0.05421
0.20543
-
1
13
2
Ketone [-C-C(=O)-C-]
-0.02248
-0.02222
-
4
10
2
Azo group [-N=N-]
-0.30036
-0.05279
-
1
3
2
Molecular Weight
---
---
53.06
697.65
-
out of range
BIOWIN5 and BIOWIN6: MITI Biodegradability Coefficients (Linear / Non-Linear)
Fragment description
Coefficient
Training set fragment count
No. of instances
of each bond
found for the
current substanceLinear
Non-Linear
Min
Max
No. of compounds in training set containing the fragment
Ester [-C(=O)-O-C]
0.343735
2.44616254
-
3
46
4
Amide [-C(=O)-N or -C(=S)-N]
0.126629
0.88586757
-
2
24
2
Ketone [-C-C(=O)-C-]
0.117739
0.83343688
-
2
25
2
Azo group [-N=N-]
-0.045873
-10.6129184
-
1
2
2
Aromatic-H
0.008218
0.12014128
-
15
302
10
Methyl [-CH3]
0.000411
0.01942827
-
9
295
6
-CH- [linear]
-0.050672
-0.09977022
-
4
63
2
Molecular Weight
---
---
30.02
959.2
-
in range
Fragment description
Coefficient
Min
Max
No. of compounds in training set containing the fragment
No. of instances
of each bond
found for the
current substanceMolecular Weight
---
---
46.07
885.46
in range
BIOWIN (v4.10) Program Results:
==============================
SMILES : CC(=O)C(N=Nc1c(ccc(c1)C(=O)OC)C(=O)OC)C(=O)Nc2ccc(cc2)NC(=O)C(N=Nc3c(
ccc(c3)C(=O)OC)C(=O)OC)C(=O)C
MOL FOR: C34 H32 N6 O12
MOL WT : 716.67
--------------------------- BIOWIN v4.10 Results ----------------------------
Biowin1 (Linear Model Prediction) : Biodegrades Fast
Biowin2 (Non-Linear Model Prediction): Does Not Biodegrade Fast
Biowin3 (Ultimate Biodegradation Timeframe): Recalcitrant
Biowin4 (Primary Biodegradation Timeframe): Days
Biowin5 (MITI Linear Model Prediction) : Does Not Biodegrade Fast
Biowin6 (MITI Non-Linear Model Prediction): Does Not Biodegrade Fast
Biowin7 (Anaerobic Model Prediction): Does Not Biodegrade Fast
Ready Biodegradability Prediction: NO
Type |
Num |
Biowin1 Fragment description |
Coeff |
Value |
Frag |
4 |
Ester [-C(=O)-O-C] |
0.1742 |
0.6967 |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
0.2102 |
0.4203 |
Frag |
2 |
Ketone [-C-C(=O)-C-] |
0.0068 |
0.0137 |
Frag |
2 |
Azo group [-N=N-] |
-0.2418 |
-0.4837 |
MolWt |
* |
Molecular Weight Parameter |
-0.3412 |
|
Const |
* |
Equation Constant |
0.7475 |
|
Result |
Biowin1 (Linear Biodeg Probability) |
1.0534 |
Type |
Num |
Biowin2 Fragment description |
Coeff |
Value |
Frag |
4 |
Ester [-C(=O)-O-C] |
4.0795 |
16.3180 |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
2.6913 |
5.3826 |
Frag |
2 |
Ketone [-C-C(=O)-C-] |
-0.4530 |
-0.9060 |
Frag |
2 |
Azo group [-N=N-] |
-8.2194 |
-16.4388 |
MolWt |
* |
Molecular Weight Parameter |
|
-10.1767 |
Result |
Biowin2 (Non-Linear Biodeg Probability) |
0.0567 |
A probability greater than or equal to 0.5 indicates --> biodegrades fast
A probability less than 0.5 indicates --> does not biodegrade fast
Type |
Num |
Biowin3 Fragment description |
Coeff |
Value |
Frag |
4 |
Ester [-C(=O)-O-C] |
0.1402 |
0.5608 |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
-0.0542 |
-0.1084 |
Frag |
2 |
Ketone [-C-C(=O)-C-] |
-0.0225 |
-0.0450 |
Frag |
2 |
Azo group [-N=N-] |
-0.3004 |
-0.6007 |
MolWt |
* |
Molecular Weight Parameter |
|
-1.5837 |
Const |
* |
Equation Constant |
|
3.1992 |
Result |
Biowin3 (Survey Model - Ultimate Biodeg) |
1.4222 |
Type |
Num |
Biowin4 Fragment description |
Coeff |
Value |
Frag |
4 |
Ester [-C(=O)-O-C] |
0.2290 |
0.9158 |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
0.2054 |
0.4109 |
Frag |
2 |
Ketone [-C-C(=O)-C-] |
-0.0222 |
-0.0444 |
Frag |
2 |
Azo group [-N=N-] |
-0.0528 |
-0.1056 |
MolWt |
* |
Molecular Weight Parameter |
|
-1.0340 |
Const |
* |
Equation Constant |
|
3.8477 |
Result |
Biowin4 (Survey Model - Primary Biodeg) |
3.9904 |
Result classification: 5.00 -> hours 4.00 -> days 3.00 -> weeks
(primary & ultimate) 2.00 -> months 1.00 -> longer
Type |
Num |
Biowin5 Fragment description |
Coeff |
Value |
Frag |
4 |
Ester [-C(=O)-O-C] |
0.3437 |
1.3749 |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
0.1266 |
0.2533 |
Frag |
2 |
Ketone [-C-C(=O)-C-] |
0.1177 |
0.2355 |
Frag |
2 |
Azo group [-N=N-] |
-0.0459 |
-0.0917 |
Frag |
10 |
Aromatic-H |
0.0082 |
0.0822 |
Frag |
6 |
Methyl [-CH3] |
0.0004 |
0.0025 |
Frag |
2 |
-CH- [linear] |
-0.0507 |
-0.1013 |
MolWt |
* |
Molecular Weight Parameter |
|
-2.1321 |
Const |
* |
Equation Constant |
|
0.7121 |
Result |
Biowin5 (MITI Linear Biodeg Probability) |
0.3353 |
Type |
Num |
Biowin6 Fragment description |
Coeff |
Value |
Frag |
4 |
Ester [-C(=O)-O-C] |
2.4462 |
9.7846 |
Frag |
2 |
Amide [-C(=O)-N or -C(=S)-N] |
0.8859 |
1.7717 |
Frag |
2 |
Ketone [-C-C(=O)-C-] |
0.8334 |
1.6669 |
Frag |
2 |
Azo group [-N=N-] |
-10.6129 |
-21.2258 |
Frag |
10 |
Aromatic-H |
0.1201 |
1.2014 |
Frag |
6 |
Methyl [-CH3] |
0.0194 |
0.1166 |
Frag |
2 |
-CH- [linear] |
-0.0998 |
-0.1995 |
MolWt |
* |
Molecular Weight Parameter |
|
-20.6893 |
Result |
Biowin6 (MITI Non-Linear Biodeg Probability) |
0.0000 |
A probability greater than or equal to 0.5 indicates --> readily degradable
A probability less than 0.5 indicates --> not readily degradable
- Reason / purpose for cross-reference:
- data waiving: supporting information
Reference
- Endpoint:
- additional information on environmental fate and behaviour
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2021
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- other: OECD 318
- Executive summary:
At any of the time points mentioned in the TG-318, the influence of Ca is critical. Regardless of pH, the pigment is unstable in 10 mM Ca, representing high water hardness.
After 6h, the samples showed high dispersion stability in 0 mM Ca and on a lower level intermediate stability in 1 mM an 10 mM Ca.
After 24 hours the stability in 0 mM Ca became intermediate. For the samples in 1 and 10 mM Ca the stability was low.
At any of the time points mentioned in the TG-318, the influence of Ca is critical. Regardless of pH, the pigment is unstable in 10 mM Ca, representing high water hardness.
After 6h, the samples showed high dispersion stability in 0 mM Ca and on a lower level intermediate stability in 1 mM and 10 mM Ca.
After 24 hours the stability in 0 mM Ca became intermediate. For the samples in 1 and 10 mM Ca the stability was low.
Full results of the dispersion stability in the presence of NOM | |||||||
Ca(NO3)2 | Stability after 6h | Standard deviation | Stability after 15h | Standard deviation | Stability after 24h | Standard deviation | |
[mM] | [%] | [%] | [%] | [%] | [%] | [%] | |
pH 4 | 0 | 91.2 | 2.7 | 78.4 | 4.5 | 64.7 | 4.5 |
pH 4 | 1 | 16.2 | 1.5 | 5.8 | 0.3 | 2.9 | 0.4 |
pH 4 | 10 | 11.5 | 0.7 | 4.1 | 0.6 | 2.9 | 0.8 |
. | |||||||
pH 7 | 0 | 89.4 | 0.9 | 73.5 | 1.2 | 60.1 | 1.3 |
pH 7 | 1 | 13.6 | 0.5 | 4.6 | 0.4 | 2.8 | 0.4 |
pH 7 | 10 | 12.7 | 1.3 | 4.9 | 0.4 | 2.9 | 0.4 |
. | |||||||
pH 9 | 0 | 94 | 0.2 | 84.5 | 0.7 | 71.5 | 1 |
pH 9 | 1 | 13.9 | 0.9 | 5.3 | 0.5 | 3.8 | 0.4 |
pH 9 | 10 | 11.5 | 0.8 | 5.7 | 0.2 | 4.6 | 0.1 |
To rationalize the observed dispersion stability, we finally checked the particle size distribution directly in the environmental medium. We applied the NanoDefine method of Analytical Ultracentrifugation. The centrifugation parameters are given in the methods section.
As required by TG318, paragraph 31, the tested nanomaterial was pre-wetted in ultrapure water and left in the form of wet-paste for 24 h. The TG318 requires this step “to insure the proper interaction of nanomaterial surface with ultrapure water.” We visually observed incomplete wetting, and so any ensuing measurement would have been incorrect. In accord with the NanoGenoTox dispersion protocol, a drop of ethanol was added, successfully transferred the powder into a paste, which was then further diluted as specified in the TG318
The observed size distributions confirm the moderate agglomeration at 1 mM Ca, pH7, with NOM. If the particles would have been significantly dissolved, no size distribution would be observable at all by this method, which relies on the detection of the movement of particles during centrifugal separation.
Additionally, the centrifugation methods include a determination of the remaining absorption after centrifugation, fully consistent with the conventional determination of the dissolved fraction after centrifugation as recommended by the TG-318. The remaining absorption was measured at ca. 0.02. This is a fraction of 1% of the initial absorption, but actually is close to the LOD of the built-in UV/Vis detector. Considering the LOD, between 0% and 2% of the sample may have been dissolved.
All evidence combined, the results after centrifugation confirm that at least 98% of the observed dispersion stability has to be attributed to the particles, not to dissolution.
Data source
Materials and methods
Test material
- Reference substance name:
- Tetramethyl 2,2'-[1,4-phenylenebis[imino(1-acetyl-2-oxoethane-1,2-diyl)azo]]bisterephthalate
- EC Number:
- 271-176-6
- EC Name:
- Tetramethyl 2,2'-[1,4-phenylenebis[imino(1-acetyl-2-oxoethane-1,2-diyl)azo]]bisterephthalate
- Cas Number:
- 68516-73-4
- Molecular formula:
- C34H32N6O12
- IUPAC Name:
- tetramethyl 2,2'-{1,4-phenylenebis[imino(1,3-dioxobutane-2,1-diyl)diazene-2,1-diyl]}diterephthalate
- Test material form:
- solid: nanoform, no surface treatment
- Details on test material:
- - State of aggregation:
- Particle size distribution:
- Shape of particles:
- Surface area of particles: BET = 46.3 m2/g
- Crystal structure: crystalline
- Coating: none
- Batch: 13007010
- solid yellow
Constituent 1
Results and discussion
- Transformation products:
- not specified
Applicant's summary and conclusion
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.