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EC number: 238-830-2 | CAS number: 14765-30-1
- 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:
- December 21, 2012 to April 04, 2013
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-D (Determination of the "Ready" Biodegradability - Manometric Respirometry Test)
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 835.3110 (Ready Biodegradability)
- Principles of method if other than guideline:
- An optional toxicity control as suggested by OECD guideline 301 F was not performed. The validity of the study is not adversely affected.
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Name (as stated in the report): FRESKOMENTHE
Lot No. VE00243225
Purity: 99.2%
Expiry date 20 July, 2015 - Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- Fresh activated sludge from a biological waste water treatment plant treating predominantly domestic sewage (Bois-de-Bay, Satigny, Switzerland) was used. The sludge is collected in the morning, washed three times in the mineral medium (by centrifuging at 1000 g for 10 minutes, discarding the supernatant and resuspending in mineral medium) and kept aerobic until being used on the same day.
- Duration of test (contact time):
- 30 d
- Initial conc.:
- 30 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- A measured volume of inoculated mineral medium, containing a known concentration of test substance as the nominal sole source of organic carbon, is stirred in a closed flask at a constant temperature (± 1°C) for up to 30 days. Evolved carbon dioxide is absorbed in sodium hydroxide pellets. The consumption of oxygen is determined by measuring the pressure drop in the respirometer flask. The Biological Oxygen Demand (BOD), amount of oxygen taken up by the microbial population during biodegradation of the test chemical (corrected for uptake by blank inoculum, run in parallel) is expressed as a percentage of ThOD (Theoretical Oxygen Demand, calculated from the elemental composition, assuming that carbon is oxidized to carbon dioxide, hydrogen to water and nitrogen to ammonium, nitrite or nitrate).
The respirometer used during this study is an Oxitop Control System, made by Wissenschaftlich-Technische Werkstätten (WTW), Weilheim, Germany.
Test substance samples (7.65 mg, corresponding to 30.0 mg/l in 255 ml of test medium) are weighed in small aluminium boats and added directly to the test flasks of the Oxitop, whereas the reference substance (sodium benzoate) is added as 1.00 ml of a 10.2 g/l solution in mineral medium, to give a total volume of 103 ml.
Flasks are filled with 250 ml of mineral medium (flasks containing reference substance: 100 ml). Samples of test or reference substance are added. Then suspended sludge diluted to a concentration of 1.53 g/l dry matter is added. Except when the test substance has an acid or alkaline character, the pH of each flask is not measured but assumed to be the same as the mineral medium, in order not to remove any floating undissolved test substance from the test medium by dipping a glass electrode in it. Neutral test substances, even sodium benzoate, were shown not to affect the pH of the medium by more than 0.1 pH unit. Two sodium hydroxide pellets are placed in the quivers on top of the bottle, and the flasks are closed tightly with the measuring heads. The flasks are allowed to equilibrate to the test temperature. The measurement is started by programming the measuring unit of the Oxitop test flasks, and the test flasks are placed in the temperature controlled cupboard of the Oxitop system. After temperature equilibration, the controller of the instrument starts the data acquisition (time zero of the experiment).
Everyday the oxygen consumption of each flask is recorded and correct temperature and stirring are checked.
At the end of the test period, the pH of each flask is measured again. - Reference substance:
- other: Sodium benzoate (Fluka, Buchs, Switzerland, Art. No. 71300), purity : min. 99.0%.
- Remarks:
- Test concentration 100 mg/L
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 60
- Sampling time:
- 28 d
- Parameter:
- % degradation (O2 consumption)
- Value:
- 64
- Sampling time:
- 30 d
- Details on results:
- Freskomenthe did not inhibit the intrinsic respiration of the inoculum at the test concentration and was therefore considered to be non-toxic to the inoculum at the test concentration.
- Results with reference substance:
- Degradation of sodium benzoate exceeded 40% after 7 days (actual observed = 72%) and 65% after 14 days (actual observed = 84%): the activity of the inoculum was thus verified (validity criterion).
- Validity criteria fulfilled:
- yes
- Remarks:
- The repeatability validity criterion (not more than 20% difference between replicates) is fulfilled for the flasks containing test substance. Therefore, the test is considered valid.
- Interpretation of results:
- readily biodegradable
- Conclusions:
- Freskomenthe should be regarded as readily biodegradable according to this test based on the biodegradation percentage of 60% at day 28.
- Executive summary:
The Ready Biodegradability of Freskomenthe was determined by the Manometric Respirometry Test.
Freskomenthe did not inhibit the intrinsic respiration of the inoculum at the test concentration and was therefore considered to be non-toxic to the inoculum at the test concentration.
Freskomenthe undergoes 60% biodegradation after 28 days (64% after 30 days) in the test conditions. The 10-day window criterion is not fulfilled (11% biodegradation on day 9 and 49% on day 19).The 10-day time window criterion was developed on the assumption that a test substance is degraded according to a “standard” growth curve in ready biodegradability tests. The OECD Guidelines for Testing of Chemicals, Section 3. Part 1: Principles and strategies related to the testing of degradation of organic chemicals (adopted 23 March 2006), states that if a substance consists of “constituents with different chain-lengths, degree and/or site of branching or stereo-isomers, even in their most purified commercial forms” and “it is anticipated that a sequential biodegradation of the individual structures is taking place, then the 10-day window should not be applied to interpret the results of the test.” The 10-day time-window should therefore not be applied as a pass / fail criterion for Freskomenthe, which is a mixture of two diastereoisomers. Thus, Freskomenthe should be regarded as readily biodegradable according to this test based on the biodegradation percentage of 60% at day 28.
- Endpoint:
- biodegradation in water: inherent biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- 15 December 1998 to 13 January 1999
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 302 C (Inherent Biodegradability: Modified MITI Test (II))
- Deviations:
- no
- GLP compliance:
- yes
- Specific details on test material used for the study:
- Name (as stated in the report): FRESKOMENTHE
Lot No. 9000317920
Purity: 97.9% - Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- Fresh activated sludge from a biological waste water treatment plant treating predominantly domestic sewage (City of Geneva, Aïre) was used.
The sludge is collected in the morning, washed three times in the mineral medium (by centrifuging at 1000 g for 10 minutes, discarding the supernatant and resuspending in mineral medium) and kept aerobic until being used on the same day.
The dry weight of the suspended solids is determined by taking two 50 mL samples of the homogenised sludge, evaporating water on a steam bath, drying in an oven at 105 - 110°C for two hours and weighing the residue.
Dry weight of suspended solids : 4.207 g/L
To obtain a concentration of 100 mg/L (dry weight) in a 1000 mL flask, 23.77 mL of sludge is needed (inoculum). - Duration of test (contact time):
- 28 d
- Initial conc.:
- 30 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- A measured volume of inoculated mineral medium, containing a known concentration (30 mg/L) of test substance as the nominal sole source of organic carbon, is stirred in a closed flask at a constant temperature (± 1°C) for up to 28 days. The consumption of oxygen is determined by measuring the quantity of oxygen (produced electrolytically) required to maintain constant the gas volume in the respirometer flask. Evolved CO2 is absorbed in soda lime pellets. The amount of oxygen taken up by the microbial population during biodegradation of the test chemical (corrected for uptake by blank inoculum, run in parallel) is expressed as a percentage of ThOD (Theoretical Oxygen Demand, calculated from the elemental composition, assuming that carbon is oxidised to CO2 and hydrogen to H2O).
- Reference substance:
- other: Sodium benzoate (purity : min. 99.0 %).
- Remarks:
- Reference Substance test concentration 100 mg/L
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 84
- Sampling time:
- 28 d
- Remarks on result:
- other: inherently biodegradable
- Results with reference substance:
- Degradation of sodium benzoate is 85 % after 7 days and 95 % after 14 days, widely in excess of the validity criterium: the activity of the inoculum is thus verified and the test is considered as valid.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- inherently biodegradable
- Conclusions:
- FRESKOMENTHE undergoes 84 % biodegradation after 28 days in the test conditions.
Thus, FRESKOMENTHE should be regarded as inherently biodegradable according to this test. - Executive summary:
The Inherent Biodegradability of FRESKOMENTHE was determined by the Manometric Respirometry Test according to the OECD Guidelines for Testing of Chemicals, Method No. 302 C.
FRESKOMENTHE undergoes 84 % biodegradation after 28 days in the test conditions.
Thus, FRESKOMENTHE should be regarded as inherently biodegradable according to this test.
Referenceopen allclose all
Freskomenthe undergoes 60% biodegradation after 28 days (64% after 30 days) in the test conditions. The 10-day window criterion is not fulfilled (11% biodegradation on day 9 and 49% on day 19). The 10-day time window criterion was developed on the assumption that a test substance is degraded according to a “standard” growth curve in ready biodegradability tests. The OECD Guidelines for Testing of Chemicals, Section 3. Part 1: Principles and strategies related to the testing of degradation of organic chemicals (adopted 23 March 2006), states that if a substance consists of “constituents with different chain-lengths, degree and/or site of branching or stereo-isomers, even in their most purified commercial forms” and “it is anticipated that a sequential biodegradation of the individual structures is taking place, then the 10-day window should not be applied to interpret the results of the test.” The 10-day time-window should therefore not be applied as a pass / fail criterion for Freskomenthe, which is a mixture of two diastereoisomers. Thus, Freskomenthe should be regarded as readily biodegradable according to this test based on the biodegradation percentage of 60% at day 28.
Description of key information
The Ready biodegradability of Freskomenthe was studied under the stringent test conditions of the OECD 301F biodegradability screening test (Givaudan study No 12-E300, GLP. dated on April 4th, 2013). FRESKOMENTHE has been determined to be READILY Biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
- Type of water:
- freshwater
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.
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