Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 242-894-7 | CAS number: 19224-26-1
- 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:
- 3 December 2013 to 2 January 2014
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: New study performed to GLP and to internationally accepted guidelines
- 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)
- GLP compliance:
- yes (incl. QA statement)
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- sewage, predominantly domestic, non-adapted
- Details on inoculum:
- - Source of inoculum: Worlingworth sewage treatment works (Suffolk, UK), the sludge was sieved (1 mm2)
- Preparation of inoculum for exposure: after transportation to the laboratory and it was left to stand for approximately 30 minutes to allow the sewage solids to settle. A portion of the supernatant was removed and the sludge aerated until required.
- Concentration of sludge:30 mg/L in test cultures - Duration of test (contact time):
- 28 d
- Initial conc.:
- 50 other: mgO2/L (oxygen demand)
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium:mineral salts medium
- Test temperature:22 ± 2ºC
- pH: 7.45
- pH adjusted: no
- Continuous darkness: yes
Kalama® K-Flex® PG was added to two bottles containing mineral salts medium inoculated with activated sludge (30 mg solids/L) to give a nominal test concentration of 50 mgO2/L. Two control cultures contained inoculated mineral salts medium alone. Two cultures contained inoculated mineral salts medium plus the reference substance sodium benzoate (50 mgO2/L), of which one also contained Kalama® K-Flex® PG (50 mgO2/L) in order to
assess the potential inhibitory effects of the test substance on the microbial inoculum. The test system comprised of an automated system for oxygen (O2) generation and the cultures were stirred and held in a thermostatically-controlled water bath. - Reference substance:
- benzoic acid, sodium salt
- Parameter:
- % degradation (O2 consumption)
- Value:
- 7
- Sampling time:
- 1 d
- Parameter:
- % degradation (O2 consumption)
- Value:
- 32
- Sampling time:
- 2 d
- Parameter:
- % degradation (O2 consumption)
- Value:
- 60
- Sampling time:
- 7 d
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 81
- Sampling time:
- 28 d
- Results with reference substance:
- The blank-corrected oxygen demanded by the culture containing the reference substance had achieved 16.04 mgO2/500 mL or 64% of the ThOD (25 mgO2/500 mL) after 3 days of incubation and 25.8 mgO2/500 mL or 103% by Day 28. Although slightly in excess of that theoretically available (100%) this was not considered significant as it is within the level of experimental error for this study type. In the presence of Kalama® K-Flex® PG, degradation of sodium benzoate had achieved 63% by Day 5. Cumulative levels of oxygen consumption by the controls after 28 days (17.95 and 19.63 mgO2/500 mL, equivalent to 35.90 and 39.26 mgO2/L) were considered to be acceptable for this assay system. These results confirm that Kalama® K-Flex® PG was not inhibitory to the activity of the microbial inoculum and that the test was valid.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- Mean oxygen consumption in mixtures containing Kalama® K-Flex® PG was 7% of the theoretical value (25 mgO2/500 mL) after 1 day, 32% after 2 days, 60% after 7 days and 81% at the end of the test (Day 28). Therefore, Kalama® K-Flex® PG was considered to be readily biodegradable under the conditions of this test.
- Executive summary:
Mean oxygen consumption in mixtures containing Kalama® K-Flex® PG was 7% of the theoretical value (25 mgO2/500 mL) after 1 day, 32% after 2 days, 60% after 7 days and 81% at the end of the test (Day 28). Therefore, Kalama® K-Flex® PG was considered to be readily biodegradable under the conditions of this test.
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 18 April 1997 - 17 May 1997
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: The study was conducted in accordance with OECD, EC, and US EPA test guidelines, and in compliance with GLP.
- Justification for type of information:
- A discussion and report on the read across strategy is given as an attachment in IUCLID Section 13.
- Reason / purpose for cross-reference:
- read-across: supporting information
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-C (Determination of the "Ready" Biodegradability - Carbon Dioxide Evolution Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 835.3110 (Ready Biodegradability)
- Version / remarks:
- Note that the version of this guideline cited in the study report was dated January 1998 (after the testing period but prior to the report issue date).
- Deviations:
- no
- Principles of method if other than guideline:
- A preliminary test using the closed bottle method was undertaken prior to the definitive test which followed the modified Sturm procedure.
- GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): A sample of activated sludge was collected on the day before the test from Oakley STW a sewage treatment works that treats predominantly domestic waste.
- Storage conditions: Not specified.
- Storage length: Not more than one day (refer to above comment)
- Preparation of inoculum for exposure: The solids content of the sludge was determined by filtering the sludge through pre-weighed filters, then drying and re-weighing the filters. The appropriate volume of inoculum was added to the control and test vessels to give a final suspended solids concentration of 30 mg/L.
- Initial cell/biomass concentration: 30 mg/L.
- Water filtered: yes - Ultrapure water was used.
- Type and size of filter used, if any: Whatman GFC filter paper - Duration of test (contact time):
- 29 d
- Initial conc.:
- 10 other: mgC/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Remarks:
- for modified Sturm
- Parameter followed for biodegradation estimation:
- O2 consumption
- Remarks:
- for preliminary closed bottle assessment
- Details on study design:
- For definitive modified Sturm test
TEST CONDITIONS
- Composition of medium: Consistent with the medium described in OECD test guideline 301B
- Solubilising agent (type and concentration if used): Solution in acetone was prepared, but the acetone was removed by evaporation under a stream of nitrogen.
- Test temperature: 21.1 - 22.9°C
- pH: 7.6 at the start, 7.3 and 7.5 at the end of the test.
- pH adjusted: no
- Aeration of dilution water: Air flow rate was between 30 to 46 mL/minute
- Suspended solids concentration: 30 mg/L
- Continuous darkness: yes
TEST SYSTEM
- Culturing apparatus: Glass bottles
- Number of culture flasks/concentration: 2
- Method used to create aerobic conditions: Continuous flushing with treated air through an air inlet tube reaching approximately 10 cm under the liquid surface.
- Measuring equipment: CO2 evolution measured by trap system described below.
- Test performed in open system: An air outlet was located just below the stopper of each test flask.
- Details of trap for CO2 and volatile organics if used: Three Drechsel bottles in series, each containing 100 mL of 0.025N Barium hydroxide.
SAMPLING
- Sampling frequency: Samples taken on days 2, 3, 4, 6, 10, 12, 14, 18, 24, and 28. A Sample was taken on day 29, in the abiotic phase of the test (test and control mixtures were acidified on day 28 of the test to kill the microbial inoculum and to drive off any residual carbon dioxide).
- Sampling method: The nearest of the three dechsel bottles was removed and the second connected in its place. The residual barium hydroxide
concentration in the removed bottle was determined by duplicate titrations with hydrochloric acid (0.05N) using phenolphthalein indicator.
CONTROL AND BLANK SYSTEM
- Inoculum blank: Yes (performed in duplicate)
- Abiotic sterile control: No
- Toxicity control: No - Reference substance:
- benzoic acid, sodium salt
- Remarks:
- Both both preliminary and definitive tests
- Preliminary study:
- Sodium benzoate was degraded to 54% of its ThOD (Theoretical Oxygen Demand) after five days of incubation which indicates that the inoculum was viable and exerting normal biodegradive activity. In the presence of the test material at 10 mg C/L, degradation of sodium benzoate was reduced to 10% of its ThOD
inhibited. This indicated that DPGDB was inhibitory to the inoculum under the conditions of this test.
Oxygen consumption by mixtures containing DPGDB alone at 10 mg C/L was equivalent to 6% of its ThOD which indicated that it was not readily biodegradable under the conditions of this preliminary test.
The level of oxygen consumption in bottles containing inoculated mineral salts medium alone at five days (0.3 mgO2/L) was considered to be acceptable for this assay system. - Parameter:
- % degradation (CO2 evolution)
- Value:
- 6
- Sampling time:
- 2 d
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 62
- Sampling time:
- 12 d
- Key result
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 85
- Sampling time:
- 28 d
- Key result
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 87
- Sampling time:
- 29 d
- Remarks on result:
- other: Includes residual CO2 released following acidification of medium.
- Key result
- Parameter:
- BOD5
- Value:
- 0.12 g O2/g test mat.
- Results with reference substance:
- The results obtained for the degradation of sodiurn benzoate (63% of its TC02 after 6 days and 79% after 29 days) and for cumulative CO2 production by the control mixtures (69.9 and 65.7 mg) fulfil the validity criteria for this test.
Although DPGDB appeared to be inhibitory to the inoculum in the preliminary test, it did not inhibit the biodegradation of benzoic acid in the definitive test (modified Sturm) - Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- Substances are considered to be readily degradable in the modifed Sturm test if CO2 production is equal to or greater than 60% of the theoretical value within ten days of the level achieving 10%. DPGDB met these criteria, so may be considered to be readily biodegradable.
Although DPGDB appeared to be inhibitory to the inoculum in the preliminary test, it did not inhibit the biodegradation of benzoic acid in the definitive test (modified Sturm). - Executive summary:
Key data is available for propylene glycol dibenzoate (PGDB). This data is supported by relevant information available from a structural analogue Dipropylene glycol dibenzoate (DPGDB). The justification for read across is presented as an attachment included in Section 13 of the IUCLID dossier.
A ready biodegradability test was performed to determine the biodegradability of the test material DPGDB. The study was conducted according to EC, OECD, and US EPA test guidelines, and in compliance with GLP.
The modified Sturm test DPGDB was found to have degraded by 6% after 2 days, 62% after 12 days, and by 85% at the end of the 28-day biotic phase of the test. The postive control substance, sodium benzoate, which was analysed contemporaneously degraded rapidly (63% degradation after 6 days), and confirmed that the inoculum was viable and that the test was valid.
Substances are considered to be readily degradable in this test if CO2 production is equal to or greater than 60% of the theoretical value within ten days of the level achieving 10%. In the Modified Sturm test, DPGDB met these criteria, so may be considered to be readily biodegradable.
Referenceopen allclose all
The pH of mixtures ranged between 7.39 and 7.49 at the start of the test and 7.38 and 7.60 at the end. The temperature of the water bath was measured daily ranged from 21.9 to 22.9˚C.
Description of key information
Key data is available for propylene glycol dibenzoate (PGDB). This data is supported by relevant information available from a structural analogue Dipropylene glycol dibenzoate (DPGDB). The justification for read across is provided as an attachment included in Section 13 of the IUCLID dossier.
Mean oxygen consumption in mixtures containing Kalama® K-Flex® PG (PGDB) was 7% of the theoretical value (25 mgO2/500 mL) after 1 day, 32% after 2 days, 60% after 7 days and 81% at the end of the test (Day 28).Therefore, Kalama® K-Flex® PG was considered to be readily biodegradable under the conditions of the OECD Guideline 301 F, Ready Biodegradability: Manometric Respirometry Test (Huntingdon Life Sciences, 2014c; Klimisch score = 1).
In a modified Sturm test DPGDB (Huntingdon Life Sciences, 1998a; Klimisch score = 1) was found to have degraded by 6% after 2 days, 62% after 12 days, and by 85% at the end of the 28-day biotic phase of the test.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
Key data is available for propylene glycol dibenzoate (PGDB). This data is supported by relevant information available from a structural analogue Dipropylene glycol dibenzoate (DPGDB). The justification for read across is provided as an attachment included in Section 13 of the IUCLID dossier.
Kalama® K-Flex® PG was added to two bottles containing mineral salts medium inoculated with activated sludge (30 mg solids/L) to give a nominal test concentration of 50 mgO2/L. Two control cultures contained inoculated mineral salts medium alone. Two cultures contained inoculated mineral salts medium plus the reference substance sodium benzoate (50 mgO2/L), of which one also contained Kalama® K-Flex® PG (50 mgO2/L) in order to assess the potential inhibitory effects of the test substance on the microbial inoculum. The test system comprised of an automated system for oxygen (O2) generation and the cultures were stirred and held in a thermostatically-controlled water bath.
Mean oxygen consumption in mixtures containing Kalama® K-Flex® PG was 7% of the theoretical value (25 mgO2/500 mL) after 1 day, 32% after 2 days, 60% after 7 days and 81% at the end of the test (Day 28). Therefore, Kalama® K-Flex® PG was considered to be readily biodegradable under the conditions of this test (Huntingdon Life Sciences, 2014c; Klimisch score = 1).
In a modified Sturm test DPGDB was found to have degraded by 6% after 2 days, 62% after 12 days, and by 85% at the end of the 28-day biotic phase of the test. The positive control substance, sodium benzoate, which was analysed contemporaneously degraded rapidly (63% degradation after 6 days), and confirmed that the inoculum was viable and that the test was valid (Huntingdon Life Sciences, 1998a; Klimisch score = 1).
Substances are considered to be readily degradable in this test if CO2production is equal to or greater than 60% of the theoretical value within ten days of the level achieving 10%. In the Modified Sturm test, DPGDB met these criteria, so may be considered to be readily biodegradable. The BOD / COD studies (Huntingdon Life Sciences, 1999a, 1998b; Klimisch score = 1) show DPGDB to be inherently biodegradable and the anaerobic study showed it to be anaerobically biodegradable (Huntingdon Life Sciences, 1998c; Klimisch score = 1).
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.