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EC number: 300-496-1 | CAS number: 93940-97-7
- 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
PBT assessment
Administrative data
PBT assessment: overall result
- Name:
- 3-[[3-[[(2-cyanoethyl)amino]methyl]-3,5,5-trimethylcyclohexyl]amino]propiononitrile
- Type of composition:
- legal entity composition of the substance
- State / form:
- liquid
- >= 95 - <= 100 % (w/w)
- Reference substance:
- 3-[[3-[[(2-cyanoethyl)amino]methyl]-3,5,5-trimethylcyclohexyl]amino]propiononitrile
- Reference substance:
- 3-[[3-[[(2-cyanoethyl)amino]methyl]-3,5,5-trimethylcyclohexyl]amino]propiononitrile
- This impurity is considered relevant for the classification and labelling of the substance
- PBT status:
- the substance is not PBT / vPvB
- Justification:
Parent compound:
The available evidence on degradation is not sufficient for an assessment based on the Annex XIII criteria for persistence (P and vP). As the substance is concluded to be not readily biodegradable (according to OECD criteria), it should be considered as potentially P/vP from a precautionary point of view until further data become available.
However, the substance is not B/vB based on a measured log Kow of 2.0 (BASF SE 2017, report no. 17L00094). In addition, several QSAR calculations (calculated BCF values range between 3.0 L/kg and 40.2 L/kg, BASF SE 2016, 2017) indicate no potential for bioaccumulation.
The substance is also not T since the lowest available chronic value is >> 0.01 mg/L and the substance holds no relevant classification.
PBT / vPvB – Assessment for modelled metabolites of MIPDA (CAS 93940-97-7):
ECHA Guidance on information requirements and chemical safety assessment (v3.0, June 2017), Chapter R.11.4.1 specifies that “Constituents, impurities and additives should normally be considered relevant for the PBT/vPvB assessment when they are present in concentration of ≥ 0.1% (w/w)” […] “Similar arguments apply to relevant transformation/degradation products”.
In order to identify the relevant degradation products of MIPDA as a standard information requirement according to Column 1, Section 9.2.3. of Annex IX to REACH and for purposes of an assessment of potential PBT/vPvB properties, the metabolites were modelled using CATALOGIC 301C v11.15 – July 2018 (OASIS CATALOGIC v5.13.1.156).
Overall, the model calculated 129 metabolites (Table 1) identifying 50 metabolites as relevant degradation products in terms of PBT/vPvB assessment, with an estimated quantity of ≥0.1% (equivalent to quantity setting in OASIS CATALOGIC: ≥ 0.001 [mol/mol parent]).
Table 1: QSAR prediction for CAS-#93940-97-7 (MIPDA) using CATALOGIC 301C v11.15 – July 2018 (OASIS CATALOGIC v5.13.1.156;metabolites with a quantity > 0.001 mol/mol parent after 28 d are highlighted by grey background and bold type; metabolite no: according to (Q)SAR model Catalogic v11.15 – July 2018 (OASIS CATALOGIC v5.13.156))
#
Meta-
bolite
(no)
Smiles
Quantity
(mol/mol
parent)
Log Kow
BOD
prediction
(% after
28 d)
parent
1
CC1(C)CC(NCCC#N)CC(C)(CNCCC#N)C1
1.16E-01
1.86
23
1
23
N#CCC=O
1.31E-02
-1.01
70
2
26
NCCC#N
2.45E-01
-1.13
47
3
3
CC1(C)CC(=O)CC(C)(CNCCC#N)C1
6.91E-04
1.38
24
4
2
CC1(C)CC(N)CC(C)(CNCCC#N)C1
1.46E-01
1.88
16
5
37
CC1(CO)CC(NCCC#N)CC(C)(CNCCC#N)C1
4.52E-07
0.40
30
6
55
CC1(C)CC(NCCC#N)CC(CNCCC#N)(CO)C1
2.26E-07
0.40
30
7
76
CC1(C)CC(NCCC#N)CC(C)(CNCCC(O)=O)C1
3.08E-03
-1.11
23
8
82
CC1(C)CC(NCCC(O)=O)CC(C)(CNCCC#N)C1
3.08E-03
-1.11
25
9
87
CC1(C)CC(NCCC#N)CC(C)(CNCCC(N)=O)C1
2.02E-03
0.84
22
10
88
CC1(C)CC(NCCC(N)=O)CC(C)(CNCCC#N)C1
2.02E-03
0.84
23
11
89
CC1(C)CC(NCCC#N)CC(C)(C(O)NCCC#N)C1
3.89E-04
0.32
23
12
94
CC1(C)CC(NCCC#N)CC(C)(CNC(O)CC#N)C1
2.76E-06
0.32
32
13
100
CC1(C)CC(C)(CNCCC#N)CC(O)(NCCC#N)C1
1.04E-03
1.06
20
14
102
CC1(C)CC(NC(O)CC#N)CC(C)(CNCCC#N)C1
2.76E-06
0.32
26
15
103
CC1(C)CC(NCCC#N)OC(=O)C(C)(CNCCC#N)C1
3.06E-04
1.11
29
16
106
CC1(C)CC(C)(CNCCC#N)CC(NCCC#N)OC1=O
3.06E-04
1.11
28
17
109
CC1(C)CC(NCCC#N)CC(C)(CNCCC#N)C(=O)O1
3.06E-04
-0.64
47
18
115
CC1(C)CC(C)(CNCCC#N)CC(NCCC#N)C(=O)O1
3.89E-04
-0.64
26
19
122
CC1(C)CC(NCCC#N)C(=O)OC(C)(CNCCC#N)C1
3.89E-04
-0.64
26
20
128
CC1(C)CC(NCCC#N)CC(C)(CNCCC#N)OC1=O
3.06E-04
-0.64
35
21
24
N#CCC(O)=O
3.60E-01
-0.76
65
22
4
CC1(C)CC(=O)OCC(C)(CNCCC#N)C1
3.82E-02
0.93
23
23
27
CC1(C)CC(C)(CNCCC#N)CC(=O)OC1
3.82E-02
0.93
20
24
38
CC1(C=O)CC(NCCC#N)CC(C)(CNCCC#N)C1
4.52E-07
0.37
30
25
56
CC1(C)CC(NCCC#N)CC(CNCCC#N)(C=O)C1
2.26E-07
0.37
30
26
77
CCNCC1(C)CC(NCCC#N)CC(C)(C)C1
9.19E-04
2.84
25
27
83
CCNC1CC(C)(C)CC(C)(CNCCC#N)C1
9.19E-04
2.84
25
28
91
CC1(C)CC(=O)CC(C)(C(O)NCCC#N)C1
7.41E-04
-0.16
22
29
90
CC1(C)CC(N)CC(C)(C(O)NCCC#N)C1
4.45E-04
0.34
15
30
95
CC1(C)CC(NCCC#N)CC(C)(CN)C1
3.88E-04
1.88
24
31
101
CC1(C)CC(C)(CNCCC#N)CC(N)(O)C1
1.72E-08
1.08
24
32
104
CC(C)(CC(O)NCCC#N)CC(C)(CNCCC#N)C(O)=O
2.45E-06
-3.93
31
33
107
CC(C)(CC(C)(CC(O)NCCC#N)CNCCC#N)C(O)=O
2.45E-06
-3.93
27
34
110
CC(C)(O)CC(CC(C)(CNCCC#N)C(O)=O)NCCC#N
4.86E-05
-3.93
43
35
117
CC1(C)CC(C)(CNCCC#N)CC(=O)C(=O)O1
8.72E-04
0.91
24
36
116
CC1(C)CC(C)(CNCCC#N)CC(N)C(=O)O1
4.45E-04
-0.62
20
37
124
CC1(C)CC(=O)C(=O)OC(C)(CNCCC#N)C1
8.72E-04
0.91
22
38
123
CC1(C)CC(N)C(=O)OC(C)(CNCCC#N)C1
4.45E-04
-0.62
21
39
129
CC(C)(CC(CC(C)(O)CNCCC#N)NCCC#N)C(O)=O
4.86E-05
-3.93
33
40
25
OC(=O)CC(O)=O
1.56E-02
-1.25
100
41
5
CC(C)(CC(O)=O)CC(C)(CNCCC#N)CO
2.77E-06
-2.36
31
42
28
CC(C)(CC(C)(CC(O)=O)CNCCC#N)CO
2.77E-06
-2.36
20
43
39
CC1(C(O)=O)CC(NCCC#N)CC(C)(CNCCC#N)C1
6.37E-03
-2.58
28
44
57
CC1(C)CC(NCCC#N)CC(CNCCC#N)(C(O)=O)C1
3.18E-03
-2.58
28
45
79
CCNCC1(C)CC(=O)CC(C)(C)C1
6.91E-04
2.35
25
46
78
CCNCC1(C)CC(N)CC(C)(C)C1
1.05E-03
2.86
17
47
85
CC=O
6.91E-04
-0.17
100
48
84
CCN
1.05E-03
-0.15
63
49
92
CC1(C)CC(=O)OCC(C)(C(O)NCCC#N)C1
5.93E-04
-0.61
24
50
93
CC1(C)CC(C)(C(O)NCCC#N)CC(=O)OC1
5.93E-04
-0.61
16
51
97
CC1(C)CC(=O)CC(C)(CN)C1
7.40E-04
1.40
18
52
96
CC1(C)CC(N)CC(C)(CN)C1
4.44E-04
1.90
15
53
105
CC(C)(CC=O)CC(C)(CNCCC#N)C(O)=O
2.45E-08
-2.39
31
54
108
CC(C)(CC(C)(CC=O)CNCCC#N)C(O)=O
2.45E-08
-2.39
20
55
111
CC(C)(O)CC(N)CC(C)(CNCCC#N)C(O)=O
6.01E-04
-3.91
42
56
112
CC(C)(O)CC(=O)CC(C)(CNCCC#N)C(O)=O
6.01E-04
-4.41
49
57
113
CC(C)(O)CC(CC(C)(CN)C(O)=O)NCCC#N
6.01E-04
-3.91
40
58
114
CC(C)(O)CC(CC(C)(C=O)C(O)=O)NCCC#N
6.01E-04
-3.93
48
59
118
CC(C)(O)CC(C)(CC(=O)C(O)=O)CNCCC#N
1.05E-08
-0.98
25
60
125
CC(C)(CC(=O)C(O)=O)CC(C)(O)CNCCC#N
1.05E-08
-0.98
31
61
130
CC(C)(CC(N)CC(C)(O)CNCCC#N)C(O)=O
6.01E-04
-3.91
30
62
131
CC(C)(CC(=O)CC(C)(O)CNCCC#N)C(O)=O
6.01E-04
-4.41
32
63
132
CC(C)(CC(CC(C)(O)CN)NCCC#N)C(O)=O
6.01E-04
-3.91
28
64
133
CC(C)(CC(CC(C)(O)C=O)NCCC#N)C(O)=O
6.01E-04
-3.93
37
65
7
CC(C)(CC(O)=O)CC(C)(CNCCC#N)C(O)=O
8.95E-02
-2.72
29
66
6
CC(C)(CC(O)=O)CC(C)(CNCCC#N)C=O
2.77E-06
-2.39
31
67
30
CC(C)(CC(C)(CC(O)=O)CNCCC#N)C(O)=O
3.93E-02
-2.72
18
68
29
CC(C)(CC(C)(CC(O)=O)CNCCC#N)C=O
2.77E-06
-2.39
20
69
41
CC1(C(O)=O)CC(=O)CC(C)(CNCCC#N)C1
3.16E-12
-3.06
31
70
40
CC1(C(O)=O)CC(N)CC(C)(CNCCC#N)C1
7.29E-03
-2.56
21
71
59
CC1(C)CC(=O)CC(CNCCC#N)(C(O)=O)C1
1.58E-12
-3.06
31
72
58
CC1(C)CC(N)CC(CNCCC#N)(C(O)=O)C1
3.65E-03
-2.56
21
73
80
CCNCC1(C)CC(=O)OCC(C)(C)C1
1.93E-03
1.90
22
74
81
CCNCC1(C)CC(C)(C)CC(=O)OC1
1.93E-03
1.90
25
75
86
CC(O)=O
3.86E-08
0.09
100
76
98
CC1(C)CC(=O)OCC(C)(CN)C1
5.92E-04
0.95
17
77
99
CC1(C)CC(C)(CN)CC(=O)OC1
5.92E-04
0.95
13
78
119
CC(C)(O)CC(C)(CC(O)=O)CNCCC#N
1.48E-04
-2.85
22
79
126
CC(C)(CC(O)=O)CC(C)(O)CNCCC#N
3.38E-04
-2.85
28
80
8
CC(C)(C)CC(C)(CNCCC#N)C(O)=O
2.67E-02
-1.39
30
81
32
CC(C)(CC(C)(CC(O)=O)C=O)C(O)=O
6.60E-04
0.48
5
82
31
CC(C)(CC(C)(CC(O)=O)CN)C(O)=O
4.50E-02
-2.70
6
83
42
CC1(C(O)=O)CC(=O)OCC(C)(CNCCC#N)C1
1.75E-03
-3.51
40
84
51
CC1(CNCCC#N)CC(=O)OCC(C)(C(O)=O)C1
1.75E-03
-3.51
20
85
60
CC1(C)CC(=O)OCC(CNCCC#N)(C(O)=O)C1
8.76E-04
-3.51
25
86
65
CC1(C)CC(CNCCC#N)(C(O)=O)CC(=O)OC1
8.76E-04
-3.51
34
87
120
CC(C)(O)CC(C)(CC(O)=O)CN
4.53E-04
-2.83
12
88
121
CC(C)(O)CC(C)(CC(O)=O)C=O
4.53E-04
0.35
8
89
127
CC(C)(C)CC(C)(O)CNCCC#N
7.16E-04
1.09
29
90
10
CC(C)(C)CC(C)(C=O)C(O)=O
7.16E-04
1.81
30
91
9
CC(C)(C)CC(C)(CN)C(O)=O
3.10E-02
-1.37
22
92
33
CC(C)(CC(C)(CC(O)=O)C(O)=O)C(O)=O
1.87E-01
0.73
0
93
43
CC(CC(O)=O)(CC(C)(CNCCC#N)CO)C(O)=O
1.40E-07
-4.19
44
94
52
CC(CC(O)=O)(CC(C)(CO)C(O)=O)CNCCC#N
1.98E-03
-4.19
19
95
61
CC(C)(CC(O)=O)CC(CNCCC#N)(CO)C(O)=O
2.25E-03
-4.19
35
96
66
CC(C)(CC(CC(O)=O)(CNCCC#N)C(O)=O)CO
7.02E-08
-4.19
37
97
34
CC(CC(O)=O)(CC(C)(CO)C(O)=O)C(O)=O
1.44E-02
-0.73
0
98
44
CC(CC(O)=O)(CC(C)(CNCCC#N)C=O)C(O)=O
1.40E-07
-4.21
44
99
54
CC(CC(O)=O)(CC(C)(CO)C(O)=O)C=O
1.45E-03
-0.98
5
100
53
CC(CC(O)=O)(CC(C)(CO)C(O)=O)CN
2.26E-03
-4.17
8
101
62
CC(C)(C)CC(CNCCC#N)(CO)C(O)=O
6.71E-04
-2.85
36
102
67
CC(C)(CC(CC(O)=O)(CNCCC#N)C(O)=O)C=O
7.02E-08
-4.21
37
103
11
CC(C)(C)CC(C)(C(O)=O)C(O)=O
1.31E-07
1.48
27
104
45
CC(CC(O)=O)(CC(C)(CNCCC#N)C(O)=O)C(O)=O
1.98E-03
-3.96
42
105
63
CC(C)(C)CC(CN)(CO)C(O)=O
1.26E-03
-2.83
32
106
64
CC(C)(C)CC(CO)(C=O)C(O)=O
1.58E-03
0.35
44
107
68
CC(C)(CC(CC(O)=O)(CNCCC#N)C(O)=O)C(O)=O
9.88E-04
-3.96
34
108
12
CC(CC(C)(C)C)C(O)=O
1.71E-02
2.85
20
109
35
CC(CC(O)=O)(CC(CO)(CO)C(O)=O)C(O)=O
5.61E-04
-1.79
0
110
36
CC(CC(CC(O)=O)(CO)C(O)=O)(CO)C(O)=O
5.61E-04
-1.49
0
111
47
CC(CC(O)=O)(CC(C)(C=O)C(O)=O)C(O)=O
1.45E-03
-0.76
54
112
46
CC(CC(O)=O)(CC(C)(CN)C(O)=O)C(O)=O
2.26E-03
-3.94
36
113
70
CC(C)(CC(CC(O)=O)(C=O)C(O)=O)C(O)=O
7.24E-04
-0.76
37
114
69
CC(C)(CC(CC(O)=O)(CN)C(O)=O)C(O)=O
1.13E-03
-3.94
25
115
74
CC(C)(C)CC(CO)(C(O)=O)C(O)=O
1.26E-09
0.01
42
116
13
CC(=CC(C)(C)C)C(O)=O
1.49E-02
2.76
29
117
48
CC(CC(O)=O)(CC(C)(C(O)=O)C(O)=O)C(O)=O
8.35E-12
-0.50
51
118
71
CC(C)(CC(CC(O)=O)(C(O)=O)C(O)=O)C(O)=O
4.17E-12
-0.50
34
119
75
CC(C)(C)CC(CO)C(O)=O
1.26E-03
1.38
40
120
14
CC(C(O)C(C)(C)C)C(O)=O
1.30E-02
1.31
27
121
49
CC(CC(C)(CC(O)=O)C(O)=O)C(O)=O
5.57E-03
0.28
34
122
50
CC(CC(O)=O)CC(C)(C(O)=O)C(O)=O
2.78E-03
0.28
62
123
72
CC(C)(CC(CC(O)=O)C(O)=O)C(O)=O
2.78E-03
0.28
29
124
73
CC(C)CC(CC(O)=O)(C(O)=O)C(O)=O
1.39E-03
0.28
56
125
15
CC(=C(O)C(C)(C)C)C(O)=O
8.61E-07
1.88
41
126
16
CC(C(=O)C(C)(C)C)C(O)=O
1.13E-02
0.80
41
127
17
CC(C)(C)C(O)=O
7.21E-02
1.45
0
128
19
CCC(O)=O
7.48E-07
0.58
100
129
18
CC(C)(CO)C(O)=O
2.76E-03
-0.02
0
Persistence (“P/vP”):
In order to assess the biodegradation potential of the relevant degradation products, the (Q)SAR model CATALOGIC 301C v11.15 – July 2018 (OASIS CATALOGIC v5.13.1.156) was applied.
Concerning the applicability domain (OECD Principle 3) MIPDA is completely in the parametric and the metabolic domain (100%), but only partly in the structural domain (95%; 5% fragments were not in the training set). However, the model was used to predict potential metabolites.
- The model predicts a BOD value of 23% for MIPDA, supporting the result of the experimental data that the substance is not readily biodegradable.
- 45 of the 50 metabolites identified as relevant degradation products were calculated to be not readily biodegradable (threshold value: <60% BOD). Individual biodegradation of these metabolites was estimated to be in a range of 0% to 56% after 28 days (based on BOD).
- Five of the relevant metabolites were estimated to be readily biodegradable (threshold value: ≥60%), with individually calculated biodegradation values between 65% and 100% after 28 days (based on BOD).
In conclusion, 90% of the predicted metabolites present in concentration of ≥0.1% (equivalent to quantity setting in OASIS CATALOGIC: 0.001 [mol/mol parent]) are estimated to be not readily biodegradable while 10% of the relevant metabolites are predicted to be readily biodegradable.
The degradation products of MIPDA (CAS-# 93940-97-7) which are predicted to be not readily biodegradable should be considered as potentially P/vP from a precautionary point of view, until further data become available.
Bioaccumulation (“B/vB”):
Referring to uncharged molecules (as worst-case approach since possible ionization will even reduce the resulting log D-values), the estimation model CATALOGIC 301C v11.15 – July 2018 (OASIS CATALOGIC v5.13.1.156) calculated for the parent compound MIPDA (CAS-# 93940-97-7) a log Kow of 1.86, which is in good agreement with the experimentally determined log Kow of 2.0. Both values indicate a low potential for bioaccumulation.
Without exception, all of the 129 modelled degradation products of MIPDA were estimated to exhibit log Kow values of clearly ≤4.5 (see Table 1), thereby not fulfilling the screening criteria for bioaccumulation (B/vB) as laid down in Section 3.1 of REACH Annex XIII.
Based on the estimation data available for the modelled metabolites, all (relevant) metabolites of MIPDA are concluded to be “not B” and “not vB”.
Toxicity (“T”):
As the predicted degradation products are not likely to fulfill both the P/vP and B/vB criteria, no information was collected on their toxicity properties.
Overall conclusion:
1. Sufficient test data are available to assess the PBT/vPvB properties of MIPDA.
2. Potentially relevant degradation products were modeled using (Q)SARmodel CATALOGIC 301C v11.15 – July 2018 (OASIS CATALOGIC v5.13.1.156):
2a. Based on modeled data relevant degradation products present in concentration of ≥ 0.1% (equivalent to quantity setting in OASIS CATALOGIC: ≥0.001 [mol/mol parent]) do neither fulfill the PBT criteria (not PBT) nor the vPvB criteria (not vPvB).
2b. However, 45 predicted relevant metabolites present in concentration of ≥0.1% (equivalent to quantity setting in OASIS CATALOGIC: ≥0.001 [mol/mol parent]) should be considered as potentially P/vP from a precautionary point of view.
Reference
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