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EC number: 915-384-3 | CAS number: -
- 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
Adsorption / desorption
Administrative data
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- 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:
- QSAR prediction from a well-known and acknowledged tool.
- Qualifier:
- according to guideline
- Guideline:
- other: REACH guidance on QSARs: Chapter R.6. QSARs and grouping of chemicals
- Principles of method if other than guideline:
- The Koc of the test substance was calculated using the MCI (Molecular Connectivity Index) and Kow based approaches of the KOCWIN v 2.01 program (EPISuite v 4.11). Since the test substance is an UVCB, the Koc values were estimated for individual constituents using SMILES codes as the input parameter.
- Computational methods:
- The Koc of the test substance was calculated using the MCI (Molecular Connectivity Index) and Kow based approaches of the KOCWIN v 2.01 program (EPISuite v 4.11). Since the test substance is an UVCB, the Koc values were estimated for individual constituents using SMILES codes as the input parameter.
- Key result
- Phase system:
- other: Estimated
- Remarks:
- weighted average
- Value:
- ca. 72.64 L/kg
- Remarks on result:
- other: MCI based method (Log Koc= 1.86)
- Key result
- Phase system:
- other: Estimated
- Remarks:
- weighted average
- Value:
- ca. 62.02 L/kg
- Remarks on result:
- other: Kow based method (Log Koc= 1.79)
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The Koc of test substance was estimated using KOCWIN v 2.01 program (EPISuite v 4.11), to be 72.64 L/kg (log Koc= 1.86) with MCI method and 62.02 L/kg (log Koc= 1.79) Log Kow method.
- Executive summary:
The soil adsorption and desorption potential (Koc) of the test substance, C8-10 MIPA, was estimated using Molecular Connectivity Index (MCI) and Log Kow of the KOCWIN v 2.01 program (EPI Suite v 4.11). Since the test substance is an UVCB, the Koc values were estimated for individual constituents using SMILES codes as the input parameter. Using the MCI and log Kow methods, the predicted Koc values for all the constituents were estimated to range from 10 to 361.3 L/kg and 7.6 to 325.5 L/kg respectively. The corresponding log Koc values ranged from 1 to 2.55 and 0.88 to 2.51 (US EPA, 2019). This indicates a negligible to moderate adsorption potential (US EPA, 2012). Since all constituents meet the MW and structural fragment molecular descriptor domain criteria as defined in KOCWIN v 2.01 user guide of EPI Suite TM, the Koc predictions were considered to be moderately accurate. Given that the constituents are structurally very similar and vary only in the carbon chain length, a weighted average value, which considers the percentage of each constituent in the substance, was calculated to dampen the errors in predictions. The weighted average Koc (log Koc) values were calculated as 72.64 L/kg (log Koc= 1.86) and 62.02 L/kg (log Koc= 1.79), using the MCI and log Kow methods respectively. Based on the above information, the test substance is expected to have a moderate adsorption potential (US EPA, 2012) to soil and sediment, leading to slow migration to ground water. Overall, the Koc predictions for the test substance using KOCWIN model of EPI Suite TM can be considered to be reliable with high to moderate confidence.
Reference
Predicted value:
The estimated Koc values for the different constituents using MCI and log Kow methods were as follows:
Table 1: KOC predictions: MCI method
Constituents/Carbon chain length* |
Mean/adjusted conc |
Mole fraction Xi = (mi/Mi)/∑ (mi/Mi) |
Log Koc (MCI) |
Koc (L/kg) |
Koc x Xi |
MCI |
C6 |
5 |
0.055745358 |
1 |
10 |
0.557453578 |
MW (ID), Structural fragment (ID) |
C8 |
55 |
0.527757427 |
1.515343893 |
32.76 |
17.2893333 |
MW (ID), Structural fragment (ID) |
C10 |
45 |
0.378977051 |
2.036628895 |
108.8 |
41.23270316 |
MW (ID), Structural fragment (ID) |
C12 |
5 |
0.037520164 |
2.557867962 |
361.3 |
13.55603536 |
MW (ID), Structural fragment (ID) |
|
|
|
|
Koc= |
72.64 |
|
|
|
|
|
Log Koc= |
1.86 |
|
* Glycerol or MIPA residues have not been considered for QSAR predictions
Table 2: KOC predictions: Log Kow-based method
Constituents/Carbon chain length* |
Mean/adjusted conc |
Mole fraction Xi = (mi/Mi)/∑ (mi/Mi) |
Log Koc (log Kow) |
Koc (L/kg) |
Koc x Xi |
Log Kow |
C6 |
5 |
0.055745358 |
0.880813592 |
7.6 |
0.423664719 |
MW (ID), log Kow (ID) Structural fragment (ID) |
C8 |
55 |
0.527757427 |
1.422917981 |
26.48 |
13.97501666 |
MW (ID), log Kow (ID) Structural fragment (ID) |
C10 |
45 |
0.378977051 |
1.970486349 |
93.43 |
35.40782588 |
MW (ID), log Kow (ID) Structural fragment (ID) |
C12 |
5 |
0.037520164 |
2.512550993 |
325.5 |
12.21281347 |
MW (ID), log Kow (ID) Structural fragment (ID) |
|
|
|
|
Koc= |
62.02 |
|
|
|
|
|
Log Koc= |
1.79 |
|
* Glycerol or MIPA residues have not been considered for QSAR predictions
KOC prediction results
SMILES : O=C(NCC(O)C)CCCCC
CHEM : C6
MOL FOR: C9 H19 N1 O2
MOL WT : 173.26
--------------------------- KOCWIN v2.01 Results ---------------------------
Koc Estimate from MCI:
---------------------
First Order Molecular Connectivity Index ........... : 5.664
Non-Corrected Log Koc (0.5213 MCI + 0.60) .......... : 3.5524
Fragment Correction(s):
1 N-CO-C (aliphatic carbon) ............ : -1.0277
1 Nitrogen to Carbon (aliphatic) (-N-C).. : -0.2127
1 Aliphatic Alcohol (-C-OH) ........... : -1.3179
Corrected Log Koc .................................. : 0.9940
Over Correction Adjustment to Lower Limit Log Koc ... : 1.0000
Estimated Koc: 10 L/kg <===========
Koc Estimate from Log Kow:
-------------------------
Log Kow (Kowwin estimate) ......................... : 0.71
Non-Corrected Log Koc (0.55313 logKow + 0.9251) .... : 1.3178
Fragment Correction(s):
1 N-CO-C (aliphatic carbon) ............ : -0.0038
1 Nitrogen to Carbon (aliphatic) (-N-C).. : -0.0218
1 Aliphatic Alcohol (-C-OH) ........... : -0.4114
Corrected Log Koc .................................. : 0.8808
Estimated Koc: 7.6 L/kg <===========
SMILES : O=C(NCC(O)C)CCCCCCC
CHEM : C8
MOL FOR: C11 H23 N1 O2
MOL WT : 201.31
--------------------------- KOCWIN v2.01 Results ---------------------------
Koc Estimate from MCI:
---------------------
First Order Molecular Connectivity Index ........... : 6.664
Non-Corrected Log Koc (0.5213 MCI + 0.60) .......... : 4.0737
Fragment Correction(s):
1 N-CO-C (aliphatic carbon) ............ : -1.0277
1 Nitrogen to Carbon (aliphatic) (-N-C).. : -0.2127
1 Aliphatic Alcohol (-C-OH) ........... : -1.3179
Corrected Log Koc .................................. : 1.5153
Estimated Koc: 32.76 L/kg <===========
Koc Estimate from Log Kow:
-------------------------
Log Kow (Kowwin estimate) ......................... : 1.69
Non-Corrected Log Koc (0.55313 logKow + 0.9251) .... : 1.8599
Fragment Correction(s):
1 N-CO-C (aliphatic carbon) ............ : -0.0038
1 Nitrogen to Carbon (aliphatic) (-N-C).. : -0.0218
1 Aliphatic Alcohol (-C-OH) ........... : -0.4114
Corrected Log Koc .................................. : 1.4229
Estimated Koc: 26.48 L/kg <===========
SMILES : O=C(NCC(O)C)CCCCCCCCC
CHEM : C10
MOL FOR: C13 H27 N1 O2
MOL WT : 229.37
--------------------------- KOCWIN v2.01 Results ---------------------------
Koc Estimate from MCI:
---------------------
First Order Molecular Connectivity Index ........... : 7.664
Non-Corrected Log Koc (0.5213 MCI + 0.60) .......... : 4.5950
Fragment Correction(s):
1 N-CO-C (aliphatic carbon) ............ : -1.0277
1 Nitrogen to Carbon (aliphatic) (-N-C).. : -0.2127
1 Aliphatic Alcohol (-C-OH) ........... : -1.3179
Corrected Log Koc .................................. : 2.0366
Estimated Koc: 108.8 L/kg <===========
Koc Estimate from Log Kow:
-------------------------
Log Kow (Kowwin estimate) ......................... : 2.68
Non-Corrected Log Koc (0.55313 logKow + 0.9251) .... : 2.4075
Fragment Correction(s):
1 N-CO-C (aliphatic carbon) ............ : -0.0038
1 Nitrogen to Carbon (aliphatic) (-N-C).. : -0.0218
1 Aliphatic Alcohol (-C-OH) ........... : -0.4114
Corrected Log Koc .................................. : 1.9705
Estimated Koc: 93.43 L/kg <===========
SMILES : O=C(NCC(O)C)CCCCCCCCCCC
CHEM : C12
MOL FOR: C15 H31 N1 O2
MOL WT : 257.42
--------------------------- KOCWIN v2.01 Results ---------------------------
Koc Estimate from MCI:
---------------------
First Order Molecular Connectivity Index ........... : 8.664
Non-Corrected Log Koc (0.5213 MCI + 0.60) .......... : 5.1163
Fragment Correction(s):
1 N-CO-C (aliphatic carbon) ............ : -1.0277
1 Nitrogen to Carbon (aliphatic) (-N-C).. : -0.2127
1 Aliphatic Alcohol (-C-OH) ........... : -1.3179
Corrected Log Koc .................................. : 2.5579
Estimated Koc: 361.3 L/kg <===========
Koc Estimate from Log Kow:
-------------------------
Log Kow (Kowwin estimate) ......................... : 3.66
Non-Corrected Log Koc (0.55313 logKow + 0.9251) .... : 2.9496
Fragment Correction(s):
1 N-CO-C (aliphatic carbon) ............ : -0.0038
1 Nitrogen to Carbon (aliphatic) (-N-C).. : -0.0218
1 Aliphatic Alcohol (-C-OH) ........... : -0.4114
Corrected Log Koc .................................. : 2.5125
Estimated Koc: 325.5 L/kg <===========
Description of key information
Key value for chemical safety assessment
- Koc at 20 °C:
- 72.64
Additional information
The soil adsorption and desorption potential (Koc) of the test substance, C8-10 MIPA, was estimated using Molecular Connectivity Index (MCI) and Log Kow of the KOCWIN v 2.01 program (EPI Suite v 4.11). Since the test substance is an UVCB, the Koc values were estimated for individual constituents using SMILES codes as the input parameter. Using the MCI and log Kow methods, the predicted Koc values for all the constituents were estimated to range from 10 to 361.3 L/kg and 7.6 to 325.5 L/kg respectively. The corresponding log Koc values ranged from 1 to 2.55 and 0.88 to 2.51 (US EPA, 2019). This indicates a negligible to moderate adsorption potential (US EPA, 2012). Since all constituents meet the MW and structural fragment molecular descriptor domain criteria as defined in KOCWIN v 2.01 user guide of EPI Suite TM, the Koc predictions were considered to be moderately accurate. Given that the constituents are structurally very similar and vary only in the carbon chain length, a weighted average value, which considers the percentage of each constituent in the substance, was calculated to dampen the errors in predictions. The weighted average Koc (log Koc) values were calculated as 72.64 L/kg (log Koc = 1.86) and 62.02 L/kg (log Koc = 1.79), using the MCI and log Kow methods respectively. Based on the above information, the test substance is expected to have a moderate adsorption potential (US EPA, 2012) to soil and sediment, leading to slow migration to ground water. Overall, the Koc predictions for the test substance using KOCWIN model of EPI Suite TM can be considered to be reliable with high to moderate confidence.
The weighted average MCI estimate (Koc = 72.64 L/kg; log Koc = 1.86) was retained for risk assessment purposes as this method is more appropriate for surface active substances.
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