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EC number: 282-199-6 | CAS number: 84144-79-6
- 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
Key value for chemical safety assessment
Effects on fertility
Description of key information
The substance 1,2-Ethanediamine, N-(2-aminoethyl)-, reaction products with glycidyl tolyl ether is a multiconstituent substance which predominantly consists of secondary aliphatic amines, with the exception of one CGE dimer.
Various QSAR models were run on the identified constituents of the substance. Predictions with the CAESAR model revealed some positive predictions for developmental toxicity. The DART model profiler showed positive results of the unspecific category Known precedent reproductive and developmental toxic potential; Toluene and small alkyl toluene derivatives (8a) for all structures of the substance. And in the CAT-SAR system, for Human Developmental Toxicity the CGE-DIMER revealed equivocal results for developmental toxicity.
On the basis of positive indication for developmental effects from the various QSAR models it is proposed to conduct an OECD 414 Prenatal Developmental Toxicity Study (Annex IX 8.7.2) in order to clarify specifically this concern.
Thus, an OECD 421 Reproductive and Developmental Toxicity Screening Test would provide less information and is therefore waived in accordance with column 2 of REACH Annex VIII 8.7.1.
Link to relevant study records
- Endpoint:
- screening for reproductive / developmental toxicity
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- a screening study for reproductive/developmental toxicity does not need to be conducted because there is evidence from available information on structurally related substances, from (Q)SAR estimates or from in vitro methods that the substance may be a developmental toxicant
- Endpoint:
- reproductive toxicity, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Study period:
- 2016
- 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 adequate and reliable documentation / justification
- Justification for type of information:
- 1. SOFTWARE
Gnarus systems CAT-SAR system (http://www.gnarus-systems.com/how-it-works/cat-sar-overview/)
2. MODEL (incl. version number)
Cat-SAR Human Developmental Toxicity - Mattison (QMRF 1.1)
February 2, 2016 (QMRF 2.6)
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
ME-CGE-DETA structures with same molecular formula (C14 H25 N3 O2) and molecular weight (267.37)
2-ME-CGE-DETA
CC1=CC=CC=C1OCC(O)CNCCNCCN
3-ME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCN)=CC=C1
4-ME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCN)C=C1
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODELS
Human Teratogenicity (i.e., developmental toxicity): This model is derived from a dataset of compounds analyzed for potential human teratogenicity developed by Dr. Donald Mattison. The model contains developmental toxicity calls for 323 chemicals, 130 of which are classified as human teratogens and 193 as non-teratogens.
Ghanooni, M., D.R. Mattison, Y.P. Zhang, O.T. Macina, H.S. Rosenkranz, and G. Klopman (1997) Structural determinants associated with risk of human developmental toxicity. American Journal of Obstetrics and Gynecology, 176: 799-806.
5. APPLICABILITY DOMAIN
Generally--the applicable domain of this model is small organic molecules that would fit the general attributes of compounds contained the Human Developmental Toxicity database
Cat-SAR, unlike some other SAR expert systems, does not use default predictions. Chemicals have to be either predicted as active or inactive on account of fragments contained in their structure. If no identical fragment is found in an unknown chemical that meets rules 1-3 in section 4.4 of this QMRF, no prediction is made. In this fashion, the applicable domain is determined on a one-by-one basis.
6. ADEQUACY OF THE RESULT
Overall, the prediction of “inactive” for structural analogues of DIME-CGE-DETA were based on 17 fragments that individually related back to 263 compounds in the Human Developmental Toxicity Mattison learning set with 80 of the 739 compounds being classified as human developmental toxicants (noting redundancy wherein individual chemicals may relate to more than one fragment and cut-point value to separate active from inactive calls). - Guideline:
- other: REACH Guidance on QSARS R.6
- Principles of method if other than guideline:
- Ghanooni, M., D.R. Mattison, Y.P. Zhang, O.T. Macina, H.S. Rosenkranz, and G. Klopman (1997) Structural determinants associated with risk of human developmental toxicity. American Journal of Obstetrics and Gynecology, 176: 799-806.
- Specific details on test material used for the study:
- CGE-DIMER
CC1=CC=C(OCC(O)COC2=CC=C(C)C=C2)C=C1 - Remarks on result:
- other: QSAR Predictied Value
- Remarks on result:
- other: QSAR Predictied Value
- Remarks on result:
- other: QSAR Predictied Value
- Remarks on result:
- other: QSAR Predictied Value
- Reproductive effects observed:
- not specified
- Conclusions:
- Overall, the prediction of “equivocal” for compound CGE-DIMER was based on 17 fragments that individually related back to 263 compounds in the Human Developmental Toxicity Mattison learning set with 39 of the 263 compounds being classified as human developmental toxicants (noting redundancy wherein individual chemicals may relate to more than one fragment and cut-point value to separate active from inactive calls).
- Endpoint:
- reproductive toxicity, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Study period:
- 2016
- 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 adequate and reliable documentation / justification
- Justification for type of information:
- 1. SOFTWARE
Gnarus systems CAT-SAR system (http://www.gnarus-systems.com/how-it-works/cat-sar-overview/)
2. MODEL (incl. version number)
Cat-SAR Human Developmental Toxicity - Mattison (QMRF 1.1)
February 2, 2016 (QMRF 2.6)
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
DIME-CGE-DETA structures with same molecular formula (C24 H37 N3 O4) and molecular weight (431.58)
2-2’-DIME-CGE-DETA
CC1=CC=CC=C1OCC(O)CNCCNCCNCC(O)COC1=C(C)C=CC=C1
2-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)=CC=C1
2-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)C=C1
3-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)=CC=C1
3-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)C=C1
4-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC=C(C)C=C2)C=C1
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODELS
Human Teratogenicity (i.e., developmental toxicity): This model is derived from a dataset of compounds analyzed for potential human teratogenicity developed by Dr. Donald Mattison. The model contains developmental toxicity calls for 323 chemicals, 130 of which are classified as human teratogens and 193 as non-teratogens.
Ghanooni, M., D.R. Mattison, Y.P. Zhang, O.T. Macina, H.S. Rosenkranz, and G. Klopman (1997) Structural determinants associated with risk of human developmental toxicity. American Journal of Obstetrics and Gynecology, 176: 799-806.
5. APPLICABILITY DOMAIN
Generally--the applicable domain of this model is small organic molecules that would fit the general attributes of compounds contained the Human Developmental Toxicity database
Cat-SAR, unlike some other SAR expert systems, does not use default predictions. Chemicals have to be either predicted as active or inactive on account of fragments contained in their structure. If no identical fragment is found in an unknown chemical that meets rules 1-3 in section 4.4 of this QMRF, no prediction is made. In this fashion, the applicable domain is determined on a one-by-one basis.
6. ADEQUACY OF THE RESULT
Overall, the prediction of “inactive” for structural analogues of DIME-CGE-DETA was based on 31 fragments that individually related back to 739 compounds in the Human Developmental Toxicity Mattison learning set with 80 of the 739 compounds being classified as human developmental toxicants (noting redundancy wherein individual chemicals may relate to more than one fragment and cut-point value to separate active from inactive calls). - Guideline:
- other: REACH Guidance on QSARS R.6
- Principles of method if other than guideline:
- Ghanooni, M., D.R. Mattison, Y.P. Zhang, O.T. Macina, H.S. Rosenkranz, and G. Klopman (1997) Structural determinants associated with risk of human developmental toxicity. American Journal of Obstetrics and Gynecology, 176: 799-806.
- Specific details on test material used for the study:
- 2-2’-DIME-CGE-DETA
CC1=CC=CC=C1OCC(O)CNCCNCCNCC(O)COC1=C(C)C=CC=C1
2-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)=CC=C1
2-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)C=C1
3-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)=CC=C1
3-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)C=C1
4-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC=C(C)C=C2)C=C1 - Remarks on result:
- other: QSAR Predictied Value
- Remarks on result:
- other: QSAR Predictied Value
- Reproductive effects observed:
- not specified
- Conclusions:
- Overall, the prediction of “inactive” for structural analogues of DIME-CGE-DETA were based on 31 fragments that individually related back to 739 compounds in the Human Developmental Toxicity Mattison learning set with 80 of the 739 compounds being classified as human developmental toxicants (noting redundancy wherein individual chemicals may relate to more than one fragment and cut-point value to separate active from inactive calls).
- Endpoint:
- reproductive toxicity, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Study period:
- 2016
- 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 adequate and reliable documentation / justification
- Justification for type of information:
- 1. SOFTWARE
Gnarus systems CAT-SAR system (http://www.gnarus-systems.com/how-it-works/cat-sar-overview/)
2. MODEL (incl. version number)
Cat-SAR Human Developmental Toxicity - Mattison (QMRF 1.1)
February 2, 2016 (QMRF 2.6)
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
ME-CGE-DETA structures with same molecular formula (C14 H25 N3 O2) and molecular weight (267.37)
2-ME-CGE-DETA
CC1=CC=CC=C1OCC(O)CNCCNCCN
3-ME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCN)=CC=C1
4-ME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCN)C=C1
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODELS
Human Teratogenicity (i.e., developmental toxicity): This model is derived from a dataset of compounds analyzed for potential human teratogenicity developed by Dr. Donald Mattison. The model contains developmental toxicity calls for 323 chemicals, 130 of which are classified as human teratogens and 193 as non-teratogens.
Ghanooni, M., D.R. Mattison, Y.P. Zhang, O.T. Macina, H.S. Rosenkranz, and G. Klopman (1997) Structural determinants associated with risk of human developmental toxicity. American Journal of Obstetrics and Gynecology, 176: 799-806.
5. APPLICABILITY DOMAIN
Generally--the applicable domain of this model is small organic molecules that would fit the general attributes of compounds contained the Human Developmental Toxicity database
Cat-SAR, unlike some other SAR expert systems, does not use default predictions. Chemicals have to be either predicted as active or inactive on account of fragments contained in their structure. If no identical fragment is found in an unknown chemical that meets rules 1-3 in section 4.4 of this QMRF, no prediction is made. In this fashion, the applicable domain is determined on a one-by-one basis.
6. ADEQUACY OF THE RESULT
Overall, the prediction of “inactive” for structural analogues of DIME-CGE-DETA were based on 30 fragments that individually related back to 724 compounds in the Human Developmental Toxicity Mattison learning set with 80 of the 739 compounds being classified as human developmental toxicants (noting redundancy wherein individual chemicals may relate to more than one fragment and cut-point value to separate active from inactive calls). - Guideline:
- other: REACH Guidance on QSARS R.6
- Principles of method if other than guideline:
- Ghanooni, M., D.R. Mattison, Y.P. Zhang, O.T. Macina, H.S. Rosenkranz, and G. Klopman (1997) Structural determinants associated with risk of human developmental toxicity. American Journal of Obstetrics and Gynecology, 176: 799-806.
- Specific details on test material used for the study:
- 2-2’-DIME-CGE-DETA
CC1=CC=CC=C1OCC(O)CNCCNCCNCC(O)COC1=C(C)C=CC=C1
2-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)=CC=C1
2-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)C=C1
3-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)=CC=C1
3-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)C=C1
4-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC=C(C)C=C2)C=C1 - Clinical signs:
- not examined
- Reproductive function: oestrous cycle:
- not examined
- Remarks on result:
- other: QSAR Predictied Value
- Clinical signs:
- not examined
- Clinical signs:
- not examined
- Behaviour (functional findings):
- not examined
- Dose descriptor:
- other:
- Remarks:
- QSAR Predictied Value
- Remarks on result:
- other: QSAR Predictied Value
- Clinical signs:
- not examined
- Behaviour (functional findings):
- not examined
- Reproductive effects observed:
- not specified
- Conclusions:
- Overall, the prediction of “inactive” for compound 2-ME-CGE-DETA was based on 29 fragments that individually related back to 709 compounds in the Human Developmental Toxicity Mattison learning set with 77 of the 709 compounds being classified as human developmental toxicants (noting redundancy wherein individual chemicals may relate to more than one fragment and cut-point value to separate active from inactive calls).
Overall, the prediction of “inactive” for compound 3-ME-CGE-DETA was based on 30 fragments that individually related back to 703 compounds in the Human Developmental Toxicity Mattison learning set with 79 of the 703 compounds being classified as human developmental toxicants (noting redundancy wherein individual chemicals may relate to more than one fragment and cut-point value to separate active from inactive calls).
Overall, the prediction of “inactive” for compound 4-ME-CGE-DETA was based on 30 fragments that individually related back to 724 compounds in the Human Developmental Toxicity Mattison learning set with 80 of the 724 compounds being classified as human developmental toxicants (noting redundancy wherein individual chemicals may relate to more than one fragment and cut-point value to separate active from inactive calls). - Endpoint:
- reproductive toxicity, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Study period:
- 2017-2018
- 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 adequate and reliable documentation / justification
- Justification for type of information:
- 1. SOFTWARE
VEGA Version 1.1.4 (Build 13/2/2017)
ww.vega-qsar.eu
2. MODEL (incl. version number)
Developmental Toxicity model (CAESAR) (version 2.1.7)
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
DIME-CGE-DETA structures with same molecular formula (C24 H37 N3 O4) and molecular weight (431.58)
2-2’-DIME-CGE-DETA
CC1=CC=CC=C1OCC(O)CNCCNCCNCC(O)COC1=C(C)C=CC=C1
2-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)=CC=C1
2-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)C=C1
3-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)=CC=C1
3-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)C=C1
4-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC=C(C)C=C2)C=C1
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODELS
Developmental Toxicity model (CAESAR) (version 2.1.7)
QSAR classification model for Developmental Toxicity based on a Random Forest classification. The
model extends the original CAESAR DevTox model 1.0 developed by Istituto Mario Negri, Italy. Reference
to the original model are found on the CAESAR Project website: http://www.caesar-project.eu/ .
5. APPLICABILITY DOMAIN
The predicted structures are in the Applicability Domain of the model (VEGA reports attached)
6. ADEQUACY OF THE RESULT
Global AD Index
AD index = 0.891 - 0.897
Explanation: the predicted compounds fall into the Applicability Domain of the model.
Similarity index = 0.792 - 0.804
Explanation: only moderately similar compounds with known experimental value in the training set have been found.
Accuracy of prediction for similar molecules
Accuracy index = 1
Explanation: accuracy of prediction for similar molecules found in the training set is good.
Concordance for similar molecules
Concordance index = 1
Explanation: similar molecules found in the training set have experimental values that agree with the predicted value.
Model's descriptors range check
Descriptors range check = True
Explanation: descriptors for this compound have values inside the descriptor range of the compounds of the training set.
Atom Centered Fragments similarity check
ACF index = 1
Explanation: all atom centered fragment of the compound have been found in the compounds of the training set.
The CAESAR model predicted that the 6 molecules would display developmental toxicant effects based on read-across from experimentally-derived source data on structural analogues.
However the relevance of these results is uncertain due to structural differences with the training set molecules. - Guideline:
- other: REACH Guidance on QSARS R.6
- Principles of method if other than guideline:
- Cassano A., Manganaro A., Martin T., Young D., Piclin N., Pintore M., Bigoni D., Benfenati E. Chemistry Central Journal 2010, 4(Suppl 1):S4 (29 July 2010)
- Specific details on test material used for the study:
- 2-2’-DIME-CGE-DETA
CC1=CC=CC=C1OCC(O)CNCCNCCNCC(O)COC1=C(C)C=CC=C1
2-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)=CC=C1
2-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)C=C1
3-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)=CC=C1
3-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)C=C1
4-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC=C(C)C=C2)C=C1 - Remarks on result:
- other: QSAR Predictied Value
- Remarks on result:
- other: QSAR Predictied Value
- Reproductive effects observed:
- not specified
- Endpoint:
- reproductive toxicity, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Study period:
- 2017-2018
- 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 adequate and reliable documentation / justification
- Justification for type of information:
- 1. SOFTWARE
VEGA Version 1.1.4 (Build 13/2/2017)
ww.vega-qsar.eu
2. MODEL (incl. version number)
Estrogen Receptor-mediated effect (IRFMN/CERAPP) 1.0.0
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
CGE_DIMER
CC1=CC=C(OCC(O)COC2=CC=C(C)C=C2)C=C1
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODELS
The model providess a qualitative prediction for Estrogen Receptor mediated effect classification model
for endocrine disruptor screening. It is implemented inside the VEGA online platform, accessible at:
http://www.vega-qsar.eu/
The model has been built as a set of rules, extracted with Sarpy software from a dataset obtained from a
collection of high-quality estrogen receptor (ER) signaling data (1529 chemicals screened across 18
high-throughput screening assays integrated into a single score), from the ToxCast program (Judson RS
et al., “Integrated model of chemical perturbations of a biological pathway using 18 in vitro highthroughput screening assays for the estrogen receptor”, Toxicol Sci 148(1):137-54, 2015). The model
has been developed within the framework of the Collaborative Estrogen Receptor Activity Prediction
Project (CERAPP): Mansouri K et al., “CERAPP: Collaborative Estrogen Receptor Activity Prediction
Project”, Environ Health Perspect, 2016.
The Sarpy software has been used with a cross-validated procedure, ending with the extraction of two
sets of rules (structural alerts) related to ER-mediacted effect activity and inactivity (for a total of 61
rules). These rules have been further divided, according to their statistical significance, into a sub-set of
rules with strong statistical evidence and another one of rules with weaker evidence. These rules are
expressed SMARTS representing molecular fragments.
If at least one rule for activity is matching with the given compound, a “Active” or “Possible active”
prediction is given, depending on the statistical evidence of the rule. If no active rules are found, but at
least one rule for non-activity is matching with the given compound, a “NON-Active” or “Possible
NON-active” prediction is given, depending on the statistical evidence of the rule. If no rules are
matching at all, no prediction is provided.
5. APPLICABILITY DOMAIN
The predicted structures are in the Applicability Domain of the model (VEGA reports attached)
6. ADEQUACY OF THE RESULT
Global AD Index
AD index = 0.931
Explanation: the predicted compounds fall into the Applicability Domain of the model.
Similarity index = 0.866
Explanation: only moderately similar compounds with known experimental value in the training set have been found.
Accuracy of prediction for similar molecules
Accuracy index = 1
Explanation: accuracy of prediction for similar molecules found in the training set is good.
Concordance for similar molecules
Concordance index = 1
Explanation: similar molecules found in the training set have experimental values that agree with the predicted value.
Model's descriptors range check
Descriptors range check = True
Explanation: descriptors for this compound have values inside the descriptor range of the compounds of the training set.
Atom Centered Fragments similarity check
ACF index = 1
Explanation: all atom centered fragment of the compound have been found in the compounds of the training set.
The Prediction for all structures is NON-active, the result appears reliable.
ER non-activity alert no. 29; ER possible non-activity alert no. 3 - Guideline:
- other: REACH Guidance on QSARS R.6
- Principles of method if other than guideline:
- Mansouri K et al., “CERAPP: Collaborative Estrogen Receptor Activity Prediction Project”, Environ Health Perspect, 2016.
- Specific details on test material used for the study:
- 2-2’-DIME-CGE-DETA
CC1=CC=CC=C1OCC(O)CNCCNCCNCC(O)COC1=C(C)C=CC=C1
2-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)=CC=C1
2-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)C=C1
3-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)=CC=C1
3-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)C=C1
4-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC=C(C)C=C2)C=C1 - Remarks on result:
- other: QSAR Predictied Value
- Remarks on result:
- other: QSAR Predictied Value
- Reproductive effects observed:
- not specified
- Endpoint:
- reproductive toxicity, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Study period:
- 2017-2018
- 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 adequate and reliable documentation / justification
- Justification for type of information:
- 1. SOFTWARE
VEGA Version 1.1.4 (Build 13/2/2017)
ww.vega-qsar.eu
2. MODEL (incl. version number)
Estrogen Receptor-mediated effect (IRFMN/CERAPP) 1.0.0
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
DIME-CGE-DETA structures with same molecular formula (C24 H37 N3 O4) and molecular weight (431.58)
2-2’-DIME-CGE-DETA
CC1=CC=CC=C1OCC(O)CNCCNCCNCC(O)COC1=C(C)C=CC=C1
2-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)=CC=C1
2-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)C=C1
3-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)=CC=C1
3-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)C=C1
4-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC=C(C)C=C2)C=C1
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODELS
The model provides a qualitative prediction for Estrogen Receptor mediated effect classification model
for endocrine disruptor screening. It is implemented inside the VEGA online platform, accessible at:
http://www.vega-qsar.eu/
The model has been built as a set of rules, extracted with Sarpy software from a dataset obtained from a
collection of high-quality estrogen receptor (ER) signaling data (1529 chemicals screened across 18
high-throughput screening assays integrated into a single score), from the ToxCast program (Judson RS
et al., “Integrated model of chemical perturbations of a biological pathway using 18 in vitro highthroughput screening assays for the estrogen receptor”, Toxicol Sci 148(1):137-54, 2015). The model
has been developed within the framework of the Collaborative Estrogen Receptor Activity Prediction
Project (CERAPP): Mansouri K et al., “CERAPP: Collaborative Estrogen Receptor Activity Prediction
Project”, Environ Health Perspect, 2016.
The Sarpy software has been used with a cross-validated procedure, ending with the extraction of two
sets of rules (structural alerts) related to ER-mediacted effect activity and inactivity (for a total of 61
rules). These rules have been further divided, according to their statistical significance, into a sub-set of
rules with strong statistical evidence and another one of rules with weaker evidence. These rules are
expressed SMARTS representing molecular fragments.
If at least one rule for activity is matching with the given compound, a “Active” or “Possible active”
prediction is given, depending on the statistical evidence of the rule. If no active rules are found, but at
least one rule for non-activity is matching with the given compound, a “NON-Active” or “Possible
NON-active” prediction is given, depending on the statistical evidence of the rule. If no rules are
matching at all, no prediction is provided.
5. APPLICABILITY DOMAIN
The predicted structures are in the Applicability Domain of the model (VEGA reports attached)
6. ADEQUACY OF THE RESULT
Global AD Index
AD index = 0.903 - 0.907
Explanation: the predicted compounds fall into the Applicability Domain of the model.
Similarity index = 0.816 - 0.822
Explanation: only moderately similar compounds with known experimental value in the training set have been found.
Accuracy of prediction for similar molecules
Accuracy index = 1
Explanation: accuracy of prediction for similar molecules found in the training set is good.
Concordance for similar molecules
Concordance index = 1
Explanation: similar molecules found in the training set have experimental values that agree with the predicted value.
Model's descriptors range check
Descriptors range check = True
Explanation: descriptors for this compound have values inside the descriptor range of the compounds of the training set.
Atom Centered Fragments similarity check
ACF index = 1
Explanation: all atom centered fragment of the compound have been found in the compounds of the training set.
The Prediction for all structures is NON-active, the result appears reliable.
ER non-activity alert no. 25; ER possible non-activity alert no. 3 - Guideline:
- other: REACH Guidance on QSARS R.6
- Principles of method if other than guideline:
- Mansouri K et al., “CERAPP: Collaborative Estrogen Receptor Activity Prediction Project”, Environ Health Perspect, 2016.
- Specific details on test material used for the study:
- 2-2’-DIME-CGE-DETA
CC1=CC=CC=C1OCC(O)CNCCNCCNCC(O)COC1=C(C)C=CC=C1
2-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)=CC=C1
2-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)C=C1
3-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)=CC=C1
3-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)C=C1
4-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC=C(C)C=C2)C=C1 - Remarks on result:
- other: QSAR Predictied Value
- Remarks on result:
- other: QSAR Predictied Value
- Reproductive effects observed:
- not specified
- Endpoint:
- reproductive toxicity, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Study period:
- 2017-2018
- 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 adequate and reliable documentation / justification
- Justification for type of information:
- 1. SOFTWARE
VEGA Version 1.1.4 (Build 13/2/2017)
ww.vega-qsar.eu
2. MODEL (incl. version number)
Estrogen Receptor-mediated effect (IRFMN/CERAPP) 1.0.0
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
ME-CGE-DETA structures with same molecular formula (C14 H25 N3 O2) and molecular weight (267.37)
2-ME-CGE-DETA
CC1=CC=CC=C1OCC(O)CNCCNCCN
3-ME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCN)=CC=C1
4-ME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCN)C=C1
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODELS
The model providess a qualitative prediction for Estrogen Receptor mediated effect classification model
for endocrine disruptor screening. It is implemented inside the VEGA online platform, accessible at:
http://www.vega-qsar.eu/
The model has been built as a set of rules, extracted with Sarpy software from a dataset obtained from a
collection of high-quality estrogen receptor (ER) signaling data (1529 chemicals screened across 18
high-throughput screening assays integrated into a single score), from the ToxCast program (Judson RS
et al., “Integrated model of chemical perturbations of a biological pathway using 18 in vitro highthroughput screening assays for the estrogen receptor”, Toxicol Sci 148(1):137-54, 2015). The model
has been developed within the framework of the Collaborative Estrogen Receptor Activity Prediction
Project (CERAPP): Mansouri K et al., “CERAPP: Collaborative Estrogen Receptor Activity Prediction
Project”, Environ Health Perspect, 2016.
The Sarpy software has been used with a cross-validated procedure, ending with the extraction of two
sets of rules (structural alerts) related to ER-mediacted effect activity and inactivity (for a total of 61
rules). These rules have been further divided, according to their statistical significance, into a sub-set of
rules with strong statistical evidence and another one of rules with weaker evidence. These rules are
expressed SMARTS representing molecular fragments.
If at least one rule for activity is matching with the given compound, a “Active” or “Possible active”
prediction is given, depending on the statistical evidence of the rule. If no active rules are found, but at
least one rule for non-activity is matching with the given compound, a “NON-Active” or “Possible
NON-active” prediction is given, depending on the statistical evidence of the rule. If no rules are
matching at all, no prediction is provided.
5. APPLICABILITY DOMAIN
The predicted structures are in the Applicability Domain of the model (VEGA reports attached)
6. ADEQUACY OF THE RESULT
Global AD Index
AD index = 0.903 - 0.907
Explanation: the predicted compounds fall into the Applicability Domain of the model.
Similarity index = 0.816 - 0.822
Explanation: only moderately similar compounds with known experimental value in the training set have been found.
Accuracy of prediction for similar molecules
Accuracy index = 1
Explanation: accuracy of prediction for similar molecules found in the training set is good.
Concordance for similar molecules
Concordance index = 1
Explanation: similar molecules found in the training set have experimental values that agree with the predicted value.
Model's descriptors range check
Descriptors range check = True
Explanation: descriptors for this compound have values inside the descriptor range of the compounds of the training set.
Atom Centered Fragments similarity check
ACF index = 1
Explanation: all atom centered fragment of the compound have been found in the compounds of the training set.
The Prediction for all structures is NON-active, the result appears reliable.
ER non-activity alert no. 25; ER possible non-activity alert no. 3 - Guideline:
- other: REACH Guidance on QSARS R.6
- Principles of method if other than guideline:
- Mansouri K et al., “CERAPP: Collaborative Estrogen Receptor Activity Prediction Project”, Environ Health Perspect, 2016.
- Specific details on test material used for the study:
- 2-2’-DIME-CGE-DETA
CC1=CC=CC=C1OCC(O)CNCCNCCNCC(O)COC1=C(C)C=CC=C1
2-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)=CC=C1
2-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=C(C)C=CC=C2)C=C1
3-3’-DIME-CGE-DETA
CC1=CC(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)=CC=C1
3-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC(C)=CC=C2)C=C1
4-4’-DIME-CGE-DETA
CC1=CC=C(OCC(O)CNCCNCCNCC(O)COC2=CC=C(C)C=C2)C=C1 - Remarks on result:
- other: QSAR Predictied Value
- Remarks on result:
- other: QSAR Predictied Value
- Reproductive effects observed:
- not specified
Referenceopen allclose all
Overall, the prediction of “inactive” for structural analogues of DIME-CGE-DETA were based on 31 fragments that individually related back to 739 compounds in the Human Developmental Toxicity Mattison learning set with 80 of the 739 compounds being classified as human developmental toxicants (noting redundancy wherein individual chemicals may relate to more than one fragment and cut-point value to separate active from inactive calls).
Overall, the prediction of “inactive” for structural analogues of DIME-CGE-DETA were based on 31 fragments that individually related back to 739 compounds in the Human Developmental Toxicity Mattison learning set with 80 of the 739 compounds being classified as human developmental toxicants (noting redundancy wherein individual chemicals may relate to more than one fragment and cut-point value to separate active from inactive calls).
Overall, the prediction of “inactive” for structural analogues of DIME-CGE-DETA were based on 31 fragments that individually related back to 739 compounds in the Human Developmental Toxicity Mattison learning set with 80 of the 739 compounds being classified as human developmental toxicants (noting redundancy wherein individual chemicals may relate to more than one fragment and cut-point value to separate active from inactive calls).
The CAESAR model predicted that the 6 molecules would display developmental toxicant effects based on read-across from experimentally-derived source data on structural analogues.
Using the VEGA Estrogen Receptor-mediated effect (IRFMN/CERAPP) 1.0.0 the Prediction for all structures is NON-active, the result appears reliable.
ER non-activity alert no. 25; ER possible non-activity alert no. 3
All structures fall within the applicability domain for the model and the results are deemed reliable based on experimental data from similar compounds.
Using the VEGA Estrogen Receptor-mediated effect (IRFMN/CERAPP) 1.0.0 the Prediction for all structures is NON-active, the result appears reliable.
ER non-activity alert no. 25; ER possible non-activity alert no. 3
All structures fall within the applicability domain for the model and the results are deemed reliable based on experimental data from similar compounds.
Using the VEGA Estrogen Receptor-mediated effect (IRFMN/CERAPP) 1.0.0 the Prediction for all structures is NON-active, the result appears reliable.
ER non-activity alert no. 25; ER possible non-activity alert no. 3
All structures fall within the applicability domain for the model and the results are deemed reliable based on experimental data from similar compounds.
Effect on fertility: via oral route
- Endpoint conclusion:
- no study available
Effect on fertility: via inhalation route
- Endpoint conclusion:
- no study available
Effect on fertility: via dermal route
- Endpoint conclusion:
- no study available
Effects on developmental toxicity
Description of key information
The substance 1,2-Ethanediamine, N-(2-aminoethyl)-, reaction products with glycidyl tolyl ether is a multiconstituent substance which predominantly consists of secondary aliphatic amines, with the exception of one CGE dimer.
Various QSAR models were run on the identified constituents of the substance. Predictions with the CAESAR model revealed some positive predictions for developmental toxicity. The DART model profiler showed positive results of the unspecific category Known precedent reproductive and developmental toxic potential; Toluene and small alkyl toluene derivatives (8a) for all structures of the substance. And in the CAT-SAR system, for Human Developmental Toxicity the CGE-DIMER revealed equivocal results for developmental toxicity.
On the basis of positive indication for developmental effects from the various QSAR models it is proposed to conduct an OECD 414 Prenatal Developmental Toxicity Study (Annex IX 8.7.2) in order to clarify specifically this concern.
Thus, an OECD 421 Reproductive and Developmental Toxicity Screening Test would provide less information and is therefore waived in accordance with column 2 of REACH Annex VIII 8.7.1.
Alternative approaches are excluded based on the following considerations:
• Available GLP studies There is no experimental GLP- study regarding toxicity on reproduction or teratogenicity available
• Available non-GLP studies There is no experimental study regarding toxicity on reproduction or teratogenicity available
• Grouping and read-across Due to the concern from the QSAR calculations and the complexity of an multiconstituent read across is not further considered
• Historical human data Not available
• (Q)SAR Data provided, see above, in attached document and endpoint entries
• In vitro methods Due to the concern from the QSAR calculations and the complexity of an multiconstituent in in vitro systems, in vitro testing is not further considered
• Weight of evidence Data generated using QSAR raise a concern for developmental toxicity, which should be clarified by the proposed OECD 414 study, there is no further data available for a weight of evidence approach
• Substance-tailored exposure
driven testing [if applicable] Not applicable. In order to clarify the concern, the OECD study 414 is considered appropriate
Link to relevant study records
- Endpoint:
- developmental toxicity
- Type of information:
- experimental study planned
- Justification for type of information:
- The attached document provides evidence generated for a testing proposal for developmental toxicity (OECD 414) using weight of evidence from structurally similar substances, identified using validated QSAR models.
The substance 1,2-Ethanediamine, N-(2-aminoethyl)-, reaction products with glycidyl tolyl ether is a multiconstituent substance which predominantly consists of secondary aliphatic amines, with the exception of one CGE dimer.
Various QSAR models were run on the identified constituents of the substance. Predictions with the CAESAR model revealed some positive predictions for developmental toxicity. The DART model profiler showed positive results of the unspecific category Known precedent reproductive and developmental toxic potential; Toluene and small alkyl toluene derivatives (8a) for all structures of the substance. And in the CAT-SAR system, for Human Developmental Toxicity the CGE-DIMER revealed equivocal results for developmental toxicity.
On the basis of positive indication for developmental effects from the various QSAR models it is proposed to conduct an OECD 414 Prenatal Developmental Toxicity Study (Annex IX 8.7.2) in order to clarify specifically this concern.
Thus, an OECD 421 Reproductive and Developmental Toxicity Screening Test would provide less information and is therefore waived in accordance with column 2 of REACH Annex VIII 8.7.1.
Alternative approaches are excluded based on the following considerations:
• Available GLP studies There is no experimental GLP- study regarding toxicity on reproduction or teratogenicity available
• Available non-GLP studies There is no experimental study regarding toxicity on reproduction or teratogenicity available
• Grouping and read-across Due to the concern from the QSAR calculations and the complexity of an multiconstituent read across is not further considered
• Historical human data Not available
• (Q)SAR Data provided, see above, in attached document and endpoint entries
• In vitro methods Due to the concern from the QSAR calculations and the complexity of an multiconstituent in in vitro systems, in vitro testing is not further considered
• Weight of evidence Data generated using QSAR raise a concern for developmental toxicity, which should be clarified by the proposed OECD 414 study, there is no further data available for a weight of evidence approach
• Substance-tailored exposure
driven testing [if applicable] Not applicable. In order to clarify the concern, the OECD study 414 is considered appropriate - Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 414 (Prenatal Developmental Toxicity Study)
- Version / remarks:
- rats
- Species:
- rat
Reference
Effect on developmental toxicity: via oral route
- Endpoint conclusion:
- no study available (further information necessary)
Effect on developmental toxicity: via inhalation route
- Endpoint conclusion:
- no study available
Effect on developmental toxicity: via dermal route
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
Additional information
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.