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EC number: 203-612-8 | CAS number: 108-74-7
- 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

Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 02 March 2007 to 15 May 2007
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- The study was conducted in accordance with international guidelines in a GLP laboratory. All relevant validity criteria were met.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 306 (Biodegradability in Seawater)
- Version / remarks:
- 1992
- Deviations:
- no
- GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- natural water: marine
- Details on inoculum:
- Seawater was collected from the Burnham-on-Crouch estuary at high water. The Crouch estuary has no industrial and no river inputs. Suspended solids were removed from the raw seawater using a hydro-clone and settlement.Date of collection: 04 April 2007Storage conditions prior to test: Dark, ambient temperatureSalinity at start of test: 31 pptTemperature at start of test: 21.8 °CPre-treatment: Settled, decanted
- Duration of test (contact time):
- 28 d
- Initial conc.:
- 3.04 mg/L
- Based on:
- ThOD
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- Replicate standard BOD bottles were filled with the test concentration, prepared by addition of a sample stock solution to dilution water. A series of test bottles was prepared with dilution water only for the determination of "blank losses". To check the integrity of the test procedure, a readily biodegradable reference material, sodium acetate, was also tested.Initial dissolved oxygen concentrations were measured using a dissolved oxygen meter. The bottles were then incubated in the dark at 20 +/- 1 °C for the test duration. Further measurements of dissolved oxygen concentration were made on bottles removed after 8, 14, 21 and 28 days.
- Reference substance:
- acetic acid, sodium salt
- Remarks:
- reported as "sodium acetate"
- Preliminary study:
- Not applicable
- Test performance:
- The guideline requires that a the reference material degrades by at least 60 % of it's ThOD, and that the blank dissolved oxygen loss should not exceed 30 % of the initial oxygen concentration. Both of these criteria were satisfied for this test; a maximum value of 79 % was achieved for the reference material and the blank dissolved oxygen loss was 15.9 %.
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 65
- Sampling time:
- 8 d
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 73
- Sampling time:
- 14 d
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 66
- Sampling time:
- 21 d
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 64
- Sampling time:
- 28 d
- Details on results:
- The calculated ThOD of the test item was 819 mg O2/g.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- The test substance was determined to be radily biodegradable, achieving >60 % biodegradation within 8 days of study initiation and achieving a maximum biodegradation value of 73 % over a 28-day period.
- Executive summary:
A study was performed in accordance with OECD Guideline 306 “Biodegradability in Seawater” (Section 5.2.2.) using the closed bottle method. The test item was added to the test vessels from a stock solution and the vessels were filled with seawater with added minerals, and closed ensuring that there was no air filled head space in the vessel. Test vessels containing seawater only (blanks), and vessels containing reference item were also prepared. Initial dissolved oxygen concentrations were measured and the test vessels were then stored in the dark at 20°C for the duration of the test. Further measurements of dissolved oxygen were made after 8, 14, 21 and 28 days.
Hexahydro-1,3,5-trimethyl-1,3,4-triazine achieved 65 % biodegradation by day 8 of the study and a maximum biodegradation of 73 % by day 14. The reference material and blanks were within guideline requirements during the test confirming the validity of the study.
Based on these results, hexahydro-1,3,5-trimethyl-1,3,4-triazine is considered to be equivalent to the category of “readily biodegradable” as described in OECD 301.
Reference
Table 1. Dissolved oxygen measurements and calculated BOD values for the test substance and reference material
|
Incubation period (days) |
||||||||||
0 |
8 |
14 |
21 |
28 |
|||||||
Incubator temperature (°C) |
20.0 |
21.0 |
22.0 |
21.5 |
21.0 |
||||||
Average blank DO (mg/L) |
6.74 |
6.19 |
6.46 |
5.94 |
5.67 |
||||||
Replicate |
1 |
1 |
2 |
1 |
2 |
1 |
2 |
3 |
1 |
2 |
3 |
Test substance – DO (mg/L) |
6.74 |
4.56 |
4.59 |
4.58 |
4.52 |
4.23 |
4.35 |
4.33 |
4.11 |
4.02 |
4.07 |
Test substance – BOD (mg O2/g) |
- |
536 |
526 |
586 |
605 |
563 |
523 |
530 |
513 |
543 |
526 |
Reference material – DO (mg/L) |
6.77 |
3.63 |
3.63 |
3.25 |
3.32 |
3.12 |
3.06 |
2.95 |
2.62 |
2.74 |
2.74 |
Reference material – BOD (mg O2/g) |
- |
515 |
515 |
624 |
610 |
567 |
579 |
600 |
612 |
588 |
588 |
Table 2. % Degradation for the test substance and reference substance
|
Incubation period (days) |
|||||||||
8 |
14 |
21 |
28 |
|||||||
Replicate |
1 |
2 |
1 |
2 |
1 |
2 |
3 |
1 |
2 |
3 |
Test Substance (%) |
65 |
64 |
71 |
74 |
69 |
64 |
65 |
63 |
66 |
64 |
Average Degradation (%) |
65 |
73 |
66 |
64 |
||||||
Reference Material (%) |
66 |
66 |
80 |
78 |
73 |
74 |
77 |
79 |
75 |
75 |
Average Degradation (%) |
66 |
79 |
75 |
76 |
Description of key information
Ready Biodegradability = Readily biodegradable, OECD 306, Drake (2007) - See Section 5.2.2.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
- Type of water:
- marine water
Additional information
A study was performed in accordance with OECD Guideline 306 “Biodegradability in Seawater” (Section 5.2.2.) using the closed bottle method. The test item was added to the test vessels from a stock solution and the vessels were filled with seawater with added minerals, and closed ensuring that there was no air filled head space in the vessel. Test vessels containing seawater only (blanks), and vessels containing reference item were also prepared. Initial dissolved oxygen concentrations were measured and the test vessels were then stored in the dark at 20°C for the duration of the test. Further measurements of dissolved oxygen were made after 8, 14, 21 and 28 days.
Hexahydro-1,3,5-trimethyl-1,3,4-triazine achieved 65 % biodegradation by day 8 of the study and a maximum biodegradation of 73 % by day 14. The reference material and blanks were within guideline requirements during the test confirming the validity of the study.
Based on these results, hexahydro-1,3,5-trimethyl-1,3,4-triazine is considered to be equivalent to the category of “readily biodegradable” as described in OECD 301.
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