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EC number: 204-793-6 | CAS number: 126-57-8
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: screening tests
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The QSAR is well documented the test compound fits well within applicability domain and the QSAR is applied for a well defined endpoint
- Justification for type of information:
- QSAR prediction: migrated from IUCLID 5.6
- Principles of method if other than guideline:
- BioWin v4.10. Biowin runs 7 models: Biowin1 = linear probability model (Howard et al. (1992)); Biowin2 = nonlinear probability model (Howard et al. (1992)); Biowin3 = expert survey ultimate biodegradation model (Boethling et al. (1994)); Biowin4 = expert survey primary biodegradation model (Boethling et al. (1994)); Biowin5 = MITI linear model (Tunkel et al. (2000)); Biowin6 = MITI nonlinear model (Tunkel et al. (2000)) and Biowin7 = anaerobic biodegradation model (Meylan et al. (2007)). Howard, P.H., Boethling, R.S., Stiteler, W.M., Meylan, W.M., Hueber, A.E., Beauman, J.A., Larosche, M.E. 1992. Predictive model for aerobic biodegradability developed from a file of evaluated biodegradation data. Environ. Toxicol. Chem. 11:593-603. Boethling, R.S., Howard, P.H., Meylan, W., Stiteler, W., Beaumann, J., Tirado, N. 1994. Group contribution method for predicting probability and rate of aerobic biodegradation. Environ. Sci. Technol. 28:459-65. Tunkel, J., Howard, P.H., Boethling, R.S., Stiteler,W., Loonen, H. 2000. Predicting Ready Biodegradability in the Japanese Ministry of International Trade and Industry Test. Environ. Toxicol. Chem. 19:2478-2485. Meylan, W., Boethling, R.S., Aronson, D., Howard, P., Tunkel, J. 2007. Chemical structure-based predictive model for methanogenic anaerobic biodegradation potential. Environ. Toxicol. Chem. 26:1785-1792
- Details on study design:
- not applicable
- Interpretation of results:
- readily biodegradable
- Conclusions:
- Based on the outcome of the QSAR models, it can be concluded that the substance can be regarded as readily biodegradable.
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Well documented study according to OECD guidelines.
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- Deviations:
- yes
- Remarks:
- no toxicity test performed with inoculumn
- GLP compliance:
- no
- Remarks:
- The test was performed in accordance with the ISO/IEC 17025
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, adapted
- Details on inoculum:
- The active sludge used as inoculum, was collected directly from oxidation tank of waste water treatment plant of Novara (Acqua Novara VCO Spa). The sludge was collected the day of start test, the ph was 7,65 and the concentration of total solids was 6 g/l. In laboratory was diluted with deionised water to a final concentration of 0,92g/l. The sludge was kept in aeration for about 5 hours before being inoculated it in the different reactors (100 ml of incoculum per 3000ml of total aqueous medium).
- Duration of test (contact time):
- 28 d
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Details on study design:
- Apparatus
The apparatus used is the same described in OECD 301 B. The total volume of aqueous medium + inoculum was 3000ml in each reactor. The test is carried out at room temperature, the CO2 evolved is captured in Ba(OH)2 traps and measured by retro-titration of the residual barium hydroxide.
Test Set Up
A total of 6 reactors were used: 2 blanks, without test sample for the determination of the background respiration, 2 test samples with TMP-PA and 2 positive control with cellulose. The reactors were filled up to a total volume of 3000ml with deionised water with phosphate buffer and mineral salts, as described in OECD 301 B guideline, and 100 ml of the inoculum. - Reference substance:
- other: cellulose
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 75.98
- St. dev.:
- 2.4
- Sampling time:
- 28 d
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- At the end of the test (after 28 days) the biodegradation of the TMP-PA was 75,98% and on the basis of the obtained result it can be declared “Readily Biodegradable”.
- Executive summary:
The determination of the biodegradation in a aqueous medium of the TMP-PA, was carried out according to test method OECD 301 B (modified sturm test), and had a duration of 28 days. The test was carried out at room temperature (23°C ±2) and in parallel was tested a positive control: cellulose microcrystalline Avicell®(Merck). The inoculum used was active, in fact the positive control reached an 82% of biodegradation. The biodegradation of the TMP-PA started immediately, while the cellulose showed a “lag” phase of about 3 days. The test exceeded the validity criteria reported in OECD 301 B. In according with the guideline, the test material TMP-PA can be stated “Ready Biodegradable” in fact it reached a biodegradation level of 60% within 28 days; more specifically it reached this level in a 10 days window starting from the 10% of biodegradation as described in OECD guideline for testing. At the end of the test (28 days) the average biodegradation of the TMP-PA was 75,98%
At the end of the test (after 28 days) the biodegradation of the TMP-PA was 75,98% and on the basis of the obtained result it can be declared “Ready Biodegradable”.
Referenceopen allclose all
All functional groups and fragments of TMP pelargonate are present in the training set, so TMP pelargonate falls within the applicability domain of the QSAR.
--------------------------- BIOWIN v4.10 Results ----------------------------
Biowin1 (Linear Model Prediction): Biodegrades Fast
Biowin2 (Non-Linear Model Prediction): Biodegrades Fast
Biowin3 (Ultimate Biodegradation Timeframe): Weeks
Biowin4 (Primary Biodegradation Timeframe): Hours-Days
Biowin5 (MITI Linear Model Prediction): Readily Degradable
Biowin6 (MITI Non-Linear Model Prediction): Readily Degradable
Biowin7 (Anaerobic Model Prediction): Does Not Biodegrade Fast
Ready Biodegradability Prediction: YES
TYPE |
NUM |
Biowin1 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
3 |
Linear C4 terminal chain [CCC-CH3] |
0.1084 |
0.3253 |
Frag |
3 |
Ester [-C(=O)-O-C] |
0.1742 |
0.5225 |
Frag |
1 |
Carbon with 4 single bonds & no hydrogens |
-0.1839 |
-0.1839 |
MolWt |
* |
Molecular Weight Parameter |
|
-0.2642 |
Const |
* |
Equation Constant |
|
0.7475 |
RESULT |
|
Biowin1 (Linear Biodeg Probability) |
|
1.1473 |
TYPE |
NUM |
Biowin2 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
3 |
Linear C4 terminal chain [CCC-CH3] |
1.8437 |
5.5311 |
Frag |
3 |
Ester [-C(=O)-O-C] |
4.0795 |
12.2385 |
Frag |
1 |
Carbon with 4 single bonds & no hydrogens |
-1.7232 |
-1.7232 |
MolWt |
* |
Molecular Weight Parameter |
|
-7.8790 |
RESULT |
|
Biowin2 (Non-Linear Biodeg Probability) |
|
1.0000 |
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 |
3 |
Linear C4 terminal chain [CCC-CH3] |
0.2983 |
0.8950 |
Frag |
3 |
Ester [-C(=O)-O-C] |
0.1402 |
0.4206 |
Frag |
1 |
Carbon with 4 single bonds & no hydrogens |
-0.2121 |
-0.2121 |
MolWt |
* |
Molecular Weight Parameter |
|
-1.2262 |
Const |
* |
Equation Constant |
|
3.1992 |
RESULT |
|
Biowin3 (Survey Model - Ultimate Biodeg) |
|
3.0765 |
TYPE |
NUM |
Biowin4 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
3 |
Linear C4 terminal chain [CCC-CH3] |
0.2691 |
0.8072 |
Frag |
3 |
Ester [-C(=O)-O-C] |
0.2290 |
0.6869 |
Frag |
1 |
Carbon with 4 single bonds & no hydrogens |
-0.1534 |
-0.1534 |
MolWt |
* |
Molecular Weight Parameter |
|
-0.8005 |
Const |
* |
Equation Constant |
|
3.8477 |
RESULT |
|
Biowin4 (Survey Model - Primary Biodeg) |
|
4.3879 |
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 |
3 |
Ester [-C(=O)-O-C] |
0.3437 |
1.0312 |
Frag |
1 |
Carbon with 4 single bonds & no hydrogens |
0.0676 |
0.0676 |
Frag |
4 |
Methyl [-CH3] |
0.0004 |
0.0016 |
Frag |
25 |
-CH2- [linear] |
0.0494 |
1.2354 |
MolWt |
* |
Molecular Weight Parameter |
|
-1.6507 |
Const |
* |
Equation Constant |
|
0.7121 |
RESULT |
|
Biowin5 (MITI Linear Biodeg Probability) |
|
1.3973 |
TYPE |
NUM |
Biowin6 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
3 |
Ester [-C(=O)-O-C] |
2.4462 |
7.3385 |
Frag |
1 |
Carbon with 4 single bonds & no hydrogens |
0.3990 |
0.3990 |
Frag |
4 |
Methyl [-CH3] |
0.0194 |
0.0777 |
Frag |
25 |
-CH2- [linear] |
0.4295 |
10.7374 |
MolWt |
* |
Molecular Weight Parameter |
|
-16.0181 |
RESULT |
|
Biowin6 (MITI Non-Linear Biodeg Probability) |
|
0.9937 |
A Probability Greater Than or Equal to 0.5 indicates --> Readily Degradable
A Probability Less Than 0.5 indicates --> NOT Readily Degradable
TYPE |
NUM |
Biowin7 FRAGMENT DESCRIPTION |
COEFF |
VALUE |
Frag |
3 |
Linear C4 terminal chain [CCC-CH3] |
-0.3177 |
-0.9532 |
Frag |
3 |
Ester [-C(=O)-O-C] |
0.1719 |
0.5156 |
Frag |
1 |
Carbon with 4 single bonds & no hydrogens |
-0.3342 |
-0.3342 |
Frag |
4 |
Methyl [-CH3] |
-0.0796 |
-0.3183 |
Frag |
25 |
-CH2- [linear] |
0.0260 |
0.6497 |
Const |
* |
Equation Constant |
|
0.8361 |
RESULT |
|
Biowin7 (Anaerobic Linear Biodeg Prob) |
|
0.3957 |
A Probability Greater Than or Equal to 0.5 indicates --> Biodegrades Fast
A Probability Less Than 0.5 indicates --> Does NOT Biodegrade Fast
CO2cumulative production (mg)
Time |
T3/17 |
T3/18 |
T3/21 |
T3/22 |
T3/23 |
T3/24 |
Days |
Blank |
Blank |
TMP-PA |
TMP-PA |
Cellulose |
Cellulose |
0,00 |
0,00 |
0,00 |
0,00 |
0,00 |
0,00 |
0,00 |
3,00 |
4,02 |
4,02 |
28,05 |
42,24 |
0,61 |
12,93 |
3,50 |
6,88 |
6,49 |
47,58 |
70,95 |
2,20 |
25,03 |
4,00 |
11,06 |
10,78 |
86,41 |
119,41 |
8,31 |
57,97 |
5,00 |
13,37 |
13,64 |
137,34 |
174,46 |
38,83 |
95,54 |
6,00 |
15,40 |
17,82 |
187,17 |
221,82 |
79,31 |
129,86 |
7,00 |
19,75 |
25,14 |
235,13 |
267,30 |
115,61 |
158,62 |
10,00 |
24,42 |
31,63 |
282,10 |
322,19 |
150,70 |
190,69 |
11,00 |
27,17 |
36,03 |
305,64 |
359,65 |
168,25 |
207,68 |
13,00 |
29,76 |
40,92 |
324,61 |
391,00 |
181,12 |
224,29 |
14,00 |
31,02 |
44,11 |
336,82 |
420,97 |
187,11 |
232,16 |
18,00 |
34,71 |
49,67 |
371,80 |
463,21 |
199,10 |
247,50 |
20,00 |
37,29 |
52,20 |
388,58 |
482,85 |
205,87 |
254,82 |
25,00 |
40,59 |
54,84 |
402,88 |
504,63 |
214,50 |
265,38 |
28,00 |
42,73 |
57,20 |
411,62 |
517,77 |
222,09 |
270,87 |
Biodegradation values (%)
Time |
%Biod. |
%Biod. |
%Biod. |
%Biod. |
Days |
TMP-PA |
TMP-PA |
Cellulose |
Cellulose |
0,00 |
0,00 |
0,00 |
0,00 |
0,00 |
3,00 |
5,16 |
6,07 |
-1,43 |
3,71 |
3,50 |
8,78 |
10,21 |
-1,88 |
7,63 |
4,00 |
16,21 |
17,23 |
-1,09 |
19,57 |
5,00 |
26,60 |
25,56 |
10,61 |
34,12 |
6,00 |
36,63 |
32,59 |
26,27 |
47,10 |
7,00 |
45,68 |
38,88 |
39,04 |
56,64 |
10,00 |
54,57 |
46,72 |
51,40 |
67,66 |
11,00 |
58,86 |
52,10 |
57,25 |
73,24 |
13,00 |
62,13 |
56,48 |
61,08 |
78,59 |
14,00 |
64,28 |
60,89 |
62,66 |
80,94 |
18,00 |
70,80 |
66,86 |
65,75 |
85,40 |
20,00 |
73,85 |
69,57 |
67,51 |
87,38 |
25,00 |
76,28 |
72,56 |
69,88 |
90,53 |
28,00 |
77,68 |
74,29 |
72,12 |
91,88 |
TABLE 5.Biodegradation average values after 28 days of test
Test item |
Biodegradation (%) |
Relative Biodegradation (%) |
TMP-PA |
75,98 (±2,40) |
92,66 |
Cellulose |
82,00 (±13,97) |
100 |
Description of key information
The substance can be regarded as readily biodegradable based on the outcome of the OECD301B study by Tosin (2013).
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
The biodegradation was assessed in one experimental key study (Tosin, 2013). This is a well documented study that was carried out according to the OECD guideline 301B. At the end of the test (after 28 days) the biodegradation of the test substance TMP-PA was 76%. The QSAR supporting study suggest that the substance is readily biodegradable. Thus on the basis of the obtained result, it can be declared “Readily Biodegradable”.
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